ࡱ>  uY]Gq` 0bjbjqPqP 2::? t777p8P8888...8fTT 8c~d~(XVDbccc@@c$hI|i8PT^8^8^888bb*V+88.4 v.f. .6t,30c.XŨ Ũ.4TŨ842&XDdc88f $88f 888^8^8^8^8^8^8 Approved afforestation and reforestation baseline and monitoring methodology ARAM0007 Afforestation and Reforestation of Land Currently Under Agricultural or Pastoral Use (Version 05) I. SOURCE, DEFINITIONS AND APPLICABILITY Sources This methodology is based on the draft CDM-AR-PDD Choc-Manab Corridor Reforestation and Conservation Carbon Project whose baseline study, monitoring and verification plan and project design document were prepared by EcoSecurities Consult, Britain; Joanneum Research, Austria; ConservationInternational, USA and EcoDecision. For more information regarding the proposal and its consideration by the Executive Board please refer to case ARNM0021-rev: Choc-Manab Corridor Reforestation and Conservation Carbon Project at: < HYPERLINK "http://cdm.unfccc.int/goto/ARpropmeth" http://cdm.unfccc.int/goto/ARpropmeth>. This methodology also refers to the latest approved versions of the following tools: Procedures to demonstrate the eligibility of lands for afforestation and reforestation CDM project activities; Combined tool to identify the baseline scenario and demonstrate the additionality in A/RCDM project activities; Procedure to determine when accounting of the soil organic carbon pool may be conservatively neglected in A/R CDM project activities; Calculation of the number of sample plots for measurements within A/R CDM project activities; Tool for testing significance of GHG emissions in A/R CDM project activities. All the above-mentioned tools are available at: <HYPERLINK "http://cdm.unfccc.int/Reference/tools"http://cdm.unfccc.int/Reference/tools>. Selected Baseline Approach from Paragraph 22 of the CDM A/R Modalities and Procedures Existing or historical, as applicable, changes in carbon stocks in the carbon pools within the project boundary Definitions This methodology does not use any methodology specific definitions. Applicability This methodology is applicable to the following project activities: Afforestation or reforestation activities undertaken on agricultural or pastoral lands. The conditions under which the methodology is applicable are: The establishment of the project occurs after a period of decreasing intensity of agricultural and pastoral activities and it may be expected that the trend would be continued in the absence of the project activity. In particular: If the pre-project activity is agriculture then: Total production of crops collected from the planned project area has decreased by at least 30% during five years preceding the validation year; or Area cultivated within the planned project boundary has decreased by at least 30% during five years preceding the validation year. If the pre-project activity is pastoral activity then: The annual average number of animals present in the planned project area when expressed using the common livestock unit used in the host country has decreased by at least 30% during five years preceding the validation year. Soil organic carbon pool may be conservatively neglected in the proposed A/R CDM project activity; Flooding irrigation is not applied in the project activity; The pre-project crown cover of trees within the project boundary is less than 20% of the threshold for crown cover reported to the EB by the host Party. The latest version of the Procedure to determine when accounting of the soil organic carbon pool may be conservatively neglected in A/R CDM project activities shall be applied to demonstrate that the soil organic carbon pool may be conservatively neglected in A/R CDM project activities. II. BASELINE METHODOLOGY PROCEDURE 1. Project boundary and eligibility of land The project boundary geographically delineates the afforestation or reforestation project activity under the control of the project participants (PPs). The A/R CDM project activity may contain more than one discrete area of land. Each discrete area of land shall have a unique geographical identification. It shall be demonstrated that each discrete area of land to be included in the boundary is eligible for an A/R CDM project activity. PPs shall apply the latest version of the tool Procedures to demonstrate the eligibility of lands for afforestation and reforestation CDM project activities as approved by the Executive Board. The latest version of Guidance on the application of the definition of project boundary to A/RCDM project activities (available at: < HYPERLINK "http://cdm.unfccc.int/Reference/Guidclarif/index.html" http://cdm.unfccc.int/Reference/Guidclarif>) may be applied in identification of areas of land planned for an A/R CDM project activity. The carbon pools included in or excluded from the project boundary are shown in Table 1. Table  SEQ Table \* ARABIC 1: Selection and justification of carbon pools Carbon PoolsSelected Justification / ExplanationAbove-groundYesMajor carbon pool subjected to the project activity. PPs may explicitly select carbon stock of above-ground biomass of non-tree woody vegetation planted as a part of the A/R CDM project activity to be included in the above-ground biomass carbon pool.Below-groundYesMajor carbon pool subjected to the project activity. PPs may explicitly select carbon stock of below-ground biomass of non-tree woody vegetation planted as a part of the A/R CDM project activity to be included in the below-ground biomass carbon pool.Dead woodYes alternatively NoCarbon pool subjected to the project activity. Alternatively, this pool may be conservatively excluded under the applicability conditions.LitterYes alternatively NoCarbon pool subjected to the project activity. Alternatively, this pool may be conservatively excluded under the applicability conditions.Soil organic carbon (SOC)No alternatively Yes (only for default approach)If No - conservative approach under applicability condition. If Yes - the default approach is selected and additional applicability conditions apply (see: Chapter 5.1.5.1 Default Changes in Soil Organic Carbon Pool)The emissions sources included in or excluded from the project boundary are shown in Table 2. Any one of these sources can be neglected, i.e., accounted as zero, if the application of the most recent version of the Tool for testing significance of GHG emissions in A/RCDM project activities leads to the conclusion that the emission source is insignificant. Table  SEQ Table \* ARABIC 2: Gases considered from emissions by sources other than resulting from changes in stocks in carbon pools SourceGasIncluded/ excludedJustification / ExplanationBurning of woody biomass (i.e., excluding herbaceous biomass)CO2IncludedCarbon stock decreases due to burning are accounted as a change in carbon stockCH4IncludedNon-CO2 gas emitted from woody biomass burning N2OExcluded Potential emissions are negligibly smallIdentification of the baseline scenario and demonstration of additionality PPs shall use the most recent version of the Combined tool to identify the baseline scenario and demonstrate additionality in A/R CDM project activities. Stratification If the project activity area is not homogeneous, stratification should be carried out to improve the accuracy and the precision of biomass estimates. Different stratifications may be required for the baseline and project scenarios in order to achieve optimal accuracy of the estimates of net GHG removal by sinks. For estimation of baseline net GHG removals by sinks, or estimation of actual net GHG removals by sinks, strata should be defined on the basis of parameters that are key entry variables in any method (e.g., growth models or yield curves/tables) used to estimate changes in biomass stocks: For baseline net GHG removals by sinks. It will usually be sufficient to stratify according to area of major vegetation types because baseline removals for degraded (or degrading) land are expected to be small in comparison to project removals; For actual net GHG removals by sinks. The ex ante estimations shall be based on the project planting/management plan. The ex post stratification shall be based on the actual implementation of the project planting/management plan. The expost stratification may be affected by natural or anthropogenic impacts if they are able to add variability to growth pattern in the project area, e.g., local fires (see SectionIII.2). Further subdivision of the project strata to represent spatial variation in the distribution of the baseline or the project biomass stocks/removals is not usually warranted. However, factors impacting growth (e.g., soil type) might be useful for ex post stratification if their variability in the project area is large. For ex ante and ex post stratification, PPs may optionally make use of remote sensing data acquired close to the time the project commences and/or close to the time of occurrence of natural or anthropogenic impacts if such impacts add variability to growth pattern in the project area. Baseline Net GHG Removals by Sinks Under the applicability conditions of this methodology: Changes in carbon stock of above-ground and below-ground biomass of non-tree vegetation may be conservatively assumed to be zero for all strata in the baseline scenario; It is expected that the baseline dead wood and litter carbon pools will not show a permanent net increase. It is therefore conservative to assume that the sum of the changes in the carbon stocks of dead wood and litter carbon pools is zero for all strata in the baseline scenario; Changes in carbon stock in soil organic carbon (SOC) may be conservatively assumed to be zero for all strata in the baseline scenario. If the pre-project crown cover of trees within the project boundary is less than 20% of the threshold for crown cover reported to the EB by the host Party then the baseline net GHG removals by sinks may be accounted for as zero. Otherwise, the baseline net GHG removals by sinks will be determined as:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 1) where: ( EMBED Equation.3 Baseline net greenhouse gas removals by sinks; t CO2-e EMBED Equation.3 Sum of the carbon stock changes in above-ground and below-ground biomass of trees in the baseline; t CO2-e4.1 Carbon stock changes in above-ground and below-ground tree biomass The estimation of carbon stock changes in above-ground and below-ground tree biomass in the baseline ((CBSL,tree) will be performed as per the equations below. These equations provide for the calculations to be performed for each stratum. If there is more than one stratum in the baseline scenario, the outcome will be summed over all the strata to obtain the value for the whole project.  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 2) where:  EMBED Equation.3 Sum of the baseline annual carbon stock changes in above-ground and below-ground tree biomass for stratum i; t CO2-e EMBED Equation.3 Baseline annual net carbon stock change in above-ground and below-ground biomass for stratum i, year t; t C yr-1 EMBED Equation.3 1, 2, 3, MB strata in the baseline scenariot1, 2, 3, t* years elapsed since the start of the A/R CDM project activity44/12Ratio of molecular weight of CO2 to carbon; t CO2-e t C-1(CBSL,AG/BG,i,t is estimated using one of the following methods that can be selected on the basis of the availability of data. Method 1 (Carbon gain-loss method)  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 3) where:  EMBED Equation.3 Baseline annual carbon stock net change in above-ground and below-ground biomass for stratum i, year t; t C yr-1 EMBED Equation.3 Annual increase in above-ground and below-ground carbon due to biomass growth of living trees in stratum i, for year t; t C yr-1 Note: This is the potential growth which is greater than the observed growth. EMBED Equation.3 Annual decrease in above-ground and below-ground carbon stock of living trees due to biomass loss for stratum i, yeart; t C yr-1 Note: Conservative assumption that  EMBED Equation.3 = 0 is allowed for the baseline scenario. EMBED Equation.3 1, 2, 3, MB strata in the baseline scenariot1, 2, 3, t* years elapsed since the start of the A/R CDM project activity EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 4) where:  EMBED Equation.3 Annual increase in carbon due to biomass growth of living trees in stratumi, for yeart; tC yr-1 EMBED Equation.3 Area of baseline stratum i; ha EMBED Equation.3 Annual increment of total above-ground and below-ground dry biomass of living trees of species j, in stratum i, for yeart; t d.m. ha-1 yr-1 EMBED Equation.3 Carbon fraction of dry matter for species j; t C t-1 d.m.i1, 2, 3, MB strata in the baseline scenarioj1, 2, 3, J tree species in the baseline scenariot1, 2, 3, t* years elapsed since the start of the A/R CDM project activityand  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 5)  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 6) where:  EMBED Equation.3 Annual increment of total dry biomass of living trees of species j, in stratum i, for yeart; t d.m. ha-1 yr-1 EMBED Equation.3 Average annual above-ground dry biomass increment of living trees of speciesj, in stratumi, for year t; t d.m. ha-1 yr-1 EMBED Equation.3 Root-shoot ratio appropriate for biomass increment for species j; t d.m. t-1 d.m EMBED Equation.3 Current annual increment in volume of species j, in stratum i, for year t; m3 ha-1 yr-1 Note:  EMBED Equation.3 can be estimated as a constant annual average value over a period including the year t (Periodical Annual Increment). Note: t is likely to be different than age of individual trees in the year t.  EMBED Equation.3 Basic wood density for species j; t d.m. m-3 EMBED Equation.3 Biomass expansion factor for conversion of annual net increment (including bark) in stem biomass to total above-ground tree biomass increment for speciesj; td.m.(t d.m.)-1i1, 2, 3, MB strata in the baseline scenarioj1, 2, 3, J tree species in the baseline scenariot1, 2, 3, t* years elapsed since the start of the A/R CDM project activityIf biomass increment tables are available and applicable to the species used in the project activity, these can directly be used in Eq.  REF _Ref226785195 \h  \* MERGEFORMAT (5). Note that available data on average annual increment in the volume of speciesj in stratumi for yeart ( EMBED Equation.3 ) may be expressed as a net average annual increment (i.e., the term EMBED Equation.3  is already implicitly allowed for and shall be set to zero in Eq. REF _Ref226785241 \h  \* MERGEFORMAT (3) in order to avoid double counting). Alternatively, if the average annual increment in volume of speciesj in stratumi, for yeart ( EMBED Equation.3 ) is expressed as the gross average annual increment, then  EMBED Equation.3  may be conservatively assumed as zero. Otherwise EMBED Equation.3  must be estimated on the basis of transparent and verifiable information on the rate at which pre-project activities (or mortality) are reducing carbon stocks in existing live trees (e.g., due to harvesting for local timber consumption, or for fuelwood). Method 2 (stock change method)  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 7)  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 8)  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 9)  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 10) where:  EMBED Equation.3 Annual carbon stock change in above-ground and below-ground tree biomass for stratumi, yeart; t C yr-1 EMBED Equation.3 Total carbon stock in living biomass of trees of species j, in stratum i, calculated at yeart; t C EMBED Equation.3 Number of years between times t2 and t1; yr EMBED Equation.3 Carbon stock in above-ground tree biomass of species j, in stratum i, at yeart; tC EMBED Equation.3 Carbon stock in below-ground tree biomass of species j, in stratum i, at yeart; tC EMBED Equation.3 Area of baseline stratum i; ha EMBED Equation.3 Pre-project tree stem volume for species j, stratum i, at yeart; m3 ha-1 EMBED Equation.3 Basic wood density for species j; t d.m. m-3  EMBED Equation.3 Biomass expansion factor for conversion of stem biomass to above-ground tree biomass for tree species j; t d.m t-1 d.m EMBED Equation.3 Carbon fraction of dry matter for species j; t C t-1 d.m. EMBED Equation.3 Root-shoot ratio appropriate for biomass stock, for species j; t C t-1 Ci1, 2, 3, MB strata in the baseline scenarioj1, 2, 3, J tree species in the baseline scenariot1, 2, 3, t* years elapsed since the start of the A/R CDM project activityAn alternative way of estimating  EMBED Equation.3 is to use allometric equations:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 11) where:  EMBED Equation.3 Carbon stock in above-ground tree biomass of species j, in stratum i, at yeart; tC EMBED Equation.3 Area of baseline stratum i; ha EMBED Equation.3 Pre-project tree stand density of species j, in stratum i, at yeart; trees ha-1 EMBED Equation.3 Carbon fraction of dry matter for species j; t C t-1 d.m. EMBED Equation.3 Allometric equation for species j linking diameter at breast height (DBH) and possibly tree height (H) to above-ground biomass of living trees; t d.m. (Note: If using an average DBH in an allometric equation, the average must be calculated as the square root of the sum of the squares of the individual tree diameters making up the sample divided by their number - i.e., so called quadratic mean or root mean square).i1, 2, 3, MB strata in the baseline scenarioj1, 2, 3, J tree species in the baseline scenariot1, 2, 3, t* years elapsed since the start of the A/R CDM project activityNote that volume tables from which  EMBED Equation.3  are obtained may or may not include allowance for losses due to harvesting or mortality. Such losses may be conservatively neglected when estimating baseline removals in pre-project trees. Otherwise EMBED Equation.3  must be estimated on the basis of credible and transparent information on the rate at which pre-project activities (and mortality, if applicable) are reducing carbon stocks in existing live trees (e.g., due to harvesting for local timber consumption, or for fuelwood). 4.2 Steady state under the baseline conditions The baseline net GHG removals by sinks, if greater than zero, shall be estimated as per approach provided in Section4.1 until steady state is reached under the baseline conditions. Under steady state:  EMBED Equation.3  PPs may, on a project specific basis, assess when a steady state is reached during the crediting period. This shall be estimated on the basis of transparent and verifiable information originating as appropriate from available literature, data from comparable areas, from field measurements in the planned project area, or from other sources relevant to the baseline circumstances. If no data is available, a default period of 20 years since commencement of the CDM project activity will be applied. Actual net GHG removals by sinks Under the applicability conditions of this methodology: Changes in carbon stock of above-ground and below-ground biomass of non-tree vegetation may be conservatively assumed to be zero for all strata in the project scenario. Optionally, PPs may include changes in carbon stock of above-ground and below-ground biomass of planted non-tree woody vegetation if selected in Table 1. The actual net greenhouse gas removals by sinks shall be estimated using the equations in this section. When applying these equations for the exante calculation of net anthropogenic GHG removals by sinks, PPs shall provide estimates of the values of those parameters that are not available before the start of the crediting period and commencement of monitoring activities. PPs should retain a conservative approach in making these estimates.  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 12) where:  EMBED Equation.3 Actual net greenhouse gas removals by sinks; t CO2-e EMBED Equation.3  Sum of the changes in above-ground and below-ground tree biomass, dead wood, litter and soil organic carbon stocks in the project scenario; t CO2-e EMBED Equation.3 Increase in GHG emissions as a result of the implementation of the proposed A/RCDM project activity within the project boundary; t CO2-eNote: In this methodology Eq.  REF _Ref226785282 \h  \* MERGEFORMAT (12) is used to estimate actual net greenhouse gas removals by sinks for the period of time elapsed between project start (t = 1) and the year t = t*, t* being the year for which actual net greenhouse gas removals by sinks are estimated. The stock change method should be used to determine annual, or periodical values. 5.1 Estimation of changes in the carbon stocks The verifiable changes in the carbon stock in tree above-ground biomass and below-ground biomass, litter and soil organic carbon within the project boundary are estimated using the following approach:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 13) where:  EMBED Equation.3 Sum of the changes in carbon pools in above-ground and below-ground tree biomass, dead wood, litter and soil organic carbon in the project scenario; t CO2-e EMBED Equation.3 Annual change in carbon stock in all selected carbon pools for year t; t C yr1t1, 2, 3, t* years elapsed since the start of the A/R project activity; yr44/12Ratio of molecular weights of CO2 and carbon; t CO2-e (t C)-1(Ct shall be estimated using the following equation:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 14) where: "CtAnnual change in carbon stock in all carbon pools for year t; t C yr 1 EMBED Equation.3 Annual carbon stock change in above-ground biomass of trees for stratumi, (possibly average over a monitoring period); t C yr-1 EMBED Equation.3 Annual carbon stock change in below-ground biomass of trees for stratumi, (possibly average over a monitoring period); t C yr-1 EMBED Equation.3 Annual change in the dead wood carbon pool in stratumi, (possibly averaged over a monitoring period); t C yr-1 EMBED Equation.3 Annual change in the litter carbon pool in stratumi, (possibly averaged over a monitoring period); t C yr1 EMBED Equation.3 Annual carbon stock change in the soil organic carbon pool for stratumi, yeart; tCyr-1i1, 2, 3, MPS strata in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activityChanges in the carbon pools that are conservatively excluded from accounting shall be set equal to zero. 5.1.1 Tree Biomass The mean carbon stock in above-ground and below-ground biomass per unit area is estimated on the basis of field measurements in permanent sample plots. Two methods are available: the Biomass Expansion Factors (BEF) method and the Allometric Equations method. BEF method Step 1: Determine on the basis of available data, e.g., volume tables (exante) and measurements (expost), the diameter at breast height (DBH, at typically 1.3 m above-ground level), and also preferably height (H), of all the trees above some minimum DBH in the permanent sample plots. Step 2: Estimate the stem volume of trees  EMBED Equation.3  on the basis of available equations or yield tables (if locally derived equations or yield tables are not available use relevant regional, national or default data as appropriate). It is possible to combine Steps1 and 2 if field instruments (e.g., a relascope) that measure the volume of each tree directly are applied. Step 3: Choose BEF and root-shoot ratio (R) - see SectionII.8 for guidance on source of data. If relevant information is available the BEF and the R should be corrected for age. Step 4: Convert the stem volume of trees into carbon stock in above-ground biomass via basic wood density, the BEF and the carbon fraction:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 15) where:  EMBED Equation.3 Carbon stock in above-ground biomass of tree l, of species j, in plotsp, in stratumi at yeart; t C EMBED Equation.3  Stem volume of tree l, of species j, in plot sp, in stratum i, at yeart; m3Dj Basic wood density of species j; t d.m. m3BEF2,j Biomass expansion factor for conversion of stem biomass to above-ground tree biomass for speciesj; dimensionlessCFj Carbon fraction of biomass for tree species j; t C t-1 d.m. (IPCC default value= 0.5tC t-1 d.m.)lSequence number of trees on plot sp i1, 2, 3, MPS strata in the project scenarioj1, 2, 3, SPS tree species in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activityStep 5: Convert the carbon stock in above-ground biomass to the carbon stock in below-ground biomass via root-shoot ratio, given by:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 16) where:  EMBED Equation.3  Carbon stock in below-ground biomass of tree l, of speciesj, in plotsp, in stratumi, at yeart; t C  EMBED Equation.3  Carbon stock in above-ground biomass of tree l, of speciesj, in plotsp, in stratumi, at yeart; t C  EMBED Equation.3  Root-shoot ratio appropriate for biomass stock, for speciesj; dimensionless Step 6: Calculate carbon stock in above-ground and below-ground biomass of all trees present in plotsp in stratumi at yeart (i.e., summation over all treesl by speciesj followed by summation over all speciesj present in plotsp). EMBED Equation.3 ( SEQ "Equation"\* Arabic \* MERGEFORMAT 17) where: EMBED Equation.3Carbon stock in trees on plot sp, of stratum i, at yeart; t C EMBED Equation.3Carbon stock in above-ground biomass of tree l, of species j, in plotsp, in stratumi, at yeart; t C EMBED Equation.3 Carbon stock in below-ground biomass of tree l, of species j, in plotsp, in stratumi, at yeart; t CEMBED Equation.3Number of trees of species j, on plot sp, of stratum i, at yeartlSequence number of trees on plot sp i1, 2, 3, MPS strata in the project scenarioj1, 2, 3, SPS tree species in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activityStep 7: Calculate the mean carbon stock in tree biomass for each stratum: EMBED Equation.3 ( SEQ "Equation"\* Arabic \* MERGEFORMAT 18) where: EMBED Equation.3Carbon stock in trees in stratum i, at yeart; t C EMBED Equation.3Carbon stock in trees on plot sp of stratum i, at yeart; t C  EMBED Equation.3 Total area of all sample plots in stratum i; haAiArea of stratum i; hasp1, 2, 3, Pi sample plots in stratum i in the project scenarioi1, 2, 3, MPS strata in the project scenariot1, 2, 3, t* years elapsed since the start of the A/R CDM project activityAllometric method Step 1: Proceed as in Step 1 of the BEF Method. Step 2: Select or develop an appropriate allometric equation (if possible species-specific, or if not from a similar species) - see SectionII.8 for additional guidance. Step 3: Estimate carbon stock in above-ground biomass for each individual treel of speciesj in the sample plot located in stratumi using the selected or developed allometric equation applied to the tree dimensions determined in Step1, and sum the carbon stocks in the sample plot:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 19) where:  EMBED Equation.3 Carbon stock in above-ground biomass of trees of speciesj, on sample plotsp, of stratumi, at yeart; tC  EMBED Equation.3 Carbon fraction of dry matter for species or type j; t C t-1 d.m.  EMBED Equation.3 Allometric equation for species j linking diameter at breast height(DBH) and possibly height(H) to above-ground biomass of a living tree; td.m. i1, 2, 3, MPS strata in the project scenarioj1, 2, 3, SPS tree species in the project scenariol1, 2, 3, Nj,sp sequence number of individual trees of species j, in sample plotsp t 1, 2, 3, t* years elapsed since the start of the A/R CDM project activityStep 4: Convert the carbon stock in above-ground biomass to the carbon stock in below-ground biomass via root-shoot ratio:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 20) where:  EMBED Equation.3  Carbon stock in below-ground biomass of trees of species j, in plotsp, in stratumi, at yeart; t C  EMBED Equation.3  Carbon stock in above-ground biomass of trees of species j, in plotsp, in stratumi, at yeart; t C  EMBED Equation.3  Root-shoot ratio appropriate for biomass stock, for species j; dimensionless Step 5: Calculate total carbon stock in the biomass of all trees present in the sample plotsp in stratumi at yeart: EMBED Equation.3 ( SEQ "Equation"\* Arabic \* MERGEFORMAT 21) where: EMBED Equation.3Carbon stock in trees on plot sp, of stratum i, at yeart; t C EMBED Equation.3Carbon stock in above-ground biomass of trees of species j, in plotsp, in stratumi, at yeart; t C EMBED Equation.3 Carbon stock in below-ground biomass of trees of species j, in plotsp, in stratumi, at yeart; t Ci1, 2, 3, MPS strata in the project scenarioj1, 2, 3, SPS tree species in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activityStep 6: Calculate the mean carbon stock in tree biomass for each stratum, as per Eq. REF _Ref226785321 \h  \* MERGEFORMAT (18) - i.e., Step7 of the BEF method. For both the BEF and the allometric methods calculate:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 22) where:  EMBED Equation.3 Annual carbon stock change in above-ground biomass of trees for stratumi; tCyr-1 EMBED Equation.3 Annual carbon stock change in below-ground biomass of trees for stratumi; tCyr-1EMBED Equation.3Carbon stock in trees in stratum i, at yeart; t C  EMBED Equation.3 Number of years between monitoring time t2 and t1 (T = t2 t1); yri1, 2, 3, MPS strata in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activity5.1.2 Planted non-tree woody vegetation biomass (if selected in Table 1) The mean carbon stock in above-ground and below-ground biomass per unit area is estimated on the basis of field measurements in permanent sample plots. Step 1: Determine on the basis of available data (exante) and measurements (expost), the characteristic numerical data on planted non-tree woody vegetation, e.g., diameter at grid, breast or other height as appropriate (Dh), height(H), crown cover(CC), number of stems(NS) or any other numerical data known to be related to above-ground volume or biomass of planted non-tree woody vegetation in the permanent sample plots. The set of characteristic numerical data used by PPs is dependent on the species and the method and need not to follow the above list. The PPs shall however, provide in the PDD a description of the relationship (equation, yield tables, etc.) between measurements taken in the sample plots and the above-ground volume/biomass of planted non-tree woody vegetation, including relevant references. Step 2: Estimate the above-ground volume/biomass of planted non-tree woody vegetation on the basis of the above-mentioned equations or yield tables. It is possible to combine Steps1 and 2 if a method that directly estimates the volume/biomass of planted non-tree woody vegetation is applied. Foreign data may be used if appropriate. Step 3a: If the above-ground volume of planted non-tree woody vegetation was estimated in Step2 above, convert the volume into carbon stock in above-ground biomass via basic wood density and the carbon fraction:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 23) Step 3b: If the above-ground biomass of planted non-tree woody vegetation was estimated in Step2 above, convert the volume into carbon stock in above-ground biomass via the carbon fraction:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 24) where (for Eq.  REF _Ref226785356 \h  \* MERGEFORMAT (23) and Eq.  REF _Ref226785368 \h  \* MERGEFORMAT (24)):  EMBED Equation.3 Carbon stock in above-ground biomass of planted non-tree woody vegetationl, of speciesj, in plotsp, in stratumi, at yeart; tC non-tree1 EMBED Equation.3  Volume of planted non-tree woody individuall, of speciesj, in plotsp, in stratumi, at yeart; m3 EMBED Equation.3 Biomass of planted non-tree woody individuall, of speciesj, in plotsp, in stratumi, at yeart; td.m.Dj Basic wood density of planted non-tree woody vegetation of speciesj; td.m. m3CF Carbon fraction of biomass for planted non-tree woody vegetation; tCt1d.m. (IPCC default value= 0.49 tC t-1 d.m.)lSequence number of planted non-tree woody vegetation individuals on plotsp i1, 2, 3, MPS strata in the project scenarioj1, 2, 3, SPS tree species in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activityStep 4: Convert the carbon stock in above-ground biomass to the carbon stock in below-ground biomass via root-shoot ratio, given by:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 25) where:  EMBED Equation.3  Carbon stock in below-ground biomass of planted non-tree woody vegetationl, of speciesj, in plotsp, in stratumi, at yeart; t C  EMBED Equation.3  Carbon stock in above-ground biomass of planted non-tree woody vegetationl, of speciesj, in plotsp, in stratumi, at yeart; t C  EMBED Equation.3  Root-shoot ratio appropriate for biomass stock of planted non-tree woody vegetation, for species j; dimensionless Step 5: Calculate carbon stock in above-ground and below-ground biomass of all trees present in plotsp in stratumi at yeart (i.e., summation over all treesl by speciesj followed by summation over all speciesj present in plotsp). EMBED Equation.3 ( SEQ "Equation"\* Arabic \* MERGEFORMAT 26) where: EMBED Equation.3Carbon stock in planted non-tree woody vegetation on plotsp, of stratumi, at yeart; tC EMBED Equation.3Carbon stock in above-ground biomass of planted non-tree woody vegetationl, of speciesj, in plotsp, in stratumi, at yeart; t C EMBED Equation.3 Carbon stock in below-ground biomass of planted non-tree woody vegetationl, of speciesj,in plotsp, in stratumi, at yeart; t CEMBED Equation.3Number of planted non-tree woody vegetation of species j, on plotsp, of stratumi, at yeartlSequence number of planted non-tree woody vegetation individuals on plotsp i1, 2, 3, MPS strata in the project scenarioj1, 2, 3, SPS planted non-tree woody vegetation species in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activityStep 6: Calculate the mean carbon stock in tree biomass for each stratum: EMBED Equation.3 ( SEQ "Equation"\* Arabic \* MERGEFORMAT 27) where: EMBED Equation.3Carbon stock in planted non-tree woody vegetation in stratum i, at yeart; tC EMBED Equation.3Carbon stock in planted non-tree woody vegetation on plotsp, of stratumi, at yeart; tC  EMBED Equation.3 Total area of all sample plots in stratum i; haAiArea of stratum i; hasp1, 2, 3, Pi sample plots in stratum i in the project scenarioi1, 2, 3, MPS strata in the project scenariot1, 2, 3, t* years elapsed since the start of the A/R CDM project activityStep 7: Calculate:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 28) where:  EMBED Equation.3 Annual carbon stock change in above-ground and below-ground biomass of planted non-tree woody vegetation for stratumi, yeart (average over a monitoring period); t C yr-1EMBED Equation.3Carbon stock in planted non-tree woody vegetation in stratumi, at yeart; tC  EMBED Equation.3 Number of years between monitoring time t2 and t1 (T = t2 t1); yri1, 2, 3, MPS strata in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activity5.1.3 Dead wood (if selected in Table 1) For ex ante estimates, the changes in carbon stocks of dead wood shall be conservatively neglected. Dead wood included in the methodology comprises two components onlystanding dead wood and lying dead wood (that is, below-ground dead wood is conservatively neglected). Considering the differences in the two components, different sampling and estimation procedures shall be used to calculate the changes in dead wood biomass of the two components. For the ex post situation, the change is estimated as follows:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 29) where:  EMBED Equation.3 Annual carbon stock change in the dead wood in stratumi, (averaged over a monitoring period); t C yr-1 EMBED Equation.3 Carbon stock of dead wood in stratum i, at yeart; t C EMBED Equation.3 Number of years between monitoring time t2 and t1 (T = t2 t1); yri1, 2, 3, MPS strata in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activityThe methods to be followed in the measurement of the standing dead wood and the lying dead wood biomass are outlined below.  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 30) where:  EMBED Equation.3 Carbon stock of dead wood biomass in stratum i, at yeart; t C EMBED Equation.3 Biomass of standing dead wood in stratum i, at yeart; t d.m. EMBED Equation.3 Biomass of lying dead wood in stratum i, at yeart; t d.m. EMBED Equation.3 Carbon fraction of dry matter in dead wood; t C t-1 d.m.i1, 2, 3, MPS strata in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activity5.1.3.1 Standing dead wood  EMBED Equation.3  Step 1: Standing dead trees shall be measured on permanent sample plots (established for estimating tree biomass - see paragraph5.1.1 above) using the same criteria and monitoring frequency used for measuring live trees. The decomposed portion that corresponds to the original above-ground and below-ground biomass is discounted. Step 2: The decomposition class of the dead tree and the diameter at breast height shall be recorded and the standing dead wood is categorized under the following four decomposition classes: Tree with branches and twigs that resembles a live tree (except for leaves); Tree with no twigs, but with persistent small and large branches; Tree with large branches only; Bole only, no branches. Step 3a: For tree in the decomposition class 1 biomass should be estimated using the allometric equation for live trees. Step 3b: When the bole is in decomposition classes 2, 3 or 4, it is recommended to limit the estimate of the biomass to the main trunk of the tree. Usually, there is no allometric equations applicable for such boles and their biomass is estimated based on volume assessment. The volume of dead wood is converted to biomass using the dead wood density appropriate for the decomposition class. 5.1.3.2 Lying dead wood  EMBED Equation.3  The lying dead wood pool is highly variable, and stocks increase as the stands grow hence; its monitoring may be taken up in the first, second or subsequent monitoring periods. The volume of lying dead wood can be assessed from the following survey: Step 1: Lying dead wood should be sampled using the line intersect method (Harmon and Sexton, 1996). Two 50-m lines bisecting each plot are established and the diameters of the lying dead wood (e"5cm diameter) intersecting the lines are measured. Step 2: The dead wood is assigned to one of the three density states ds (1(sound), 2(intermediate), and 3(rotten)) using the machete test, as recommended by IPCC Good Practice Guidance for LULUCF(2003), Section4.3.3.5.3. Step 3: The volume of lying dead wood per unit area is calculated using the equation (Warren and Olsen, 1964) as modified by van Wagner (1968) separately for each density state:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 31) where:  EMBED Equation.3 Volume of lying dead wood per unit area in stratum i, at yeart; m3 ha-1 EMBED Equation.3 Diameter of piece n of dead wood along the transect in stratum i, at yeart; cmNTotal number of wood pieces intersecting the transect; dimensionless EMBED Equation.3 Length of the transect; mi1, 2, 3, MPS strata in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activityStep 4: Volume of lying dead wood shall be converted into biomass using the following relationship.  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 32) where:  EMBED Equation.3 Biomass of lying dead wood in stratum i, at yeart; t d.m. EMBED Equation.3 Volume of lying dead wood in stratum i, at yeart; m3 ha-1 EMBED Equation.3 Basic wood density of dead wood in the density class ds; t d.m. m-3 Note: To estimate density of each class, follow the procedure described in IPCCGood Practice Guidance for LULUCF (2003), Section 4.3.3.5.3. EMBED Equation.3 Area of stratum i; hadsIndex for density state: 1 (sound), 2 (intermediate) or 3 (rotten)i1, 2, 3, MPS strata in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activity5.1.4 Litter (if selected in Table 1) For ex ante estimates, the changes in carbon stocks of litter shall be conservatively neglected. For ex post estimates, four litter samples shall be collected per sample plot and well mixed into one composite sample. Samples shall be taken at the same time of the year in order to account for natural and anthropogenic influences on the litter accumulation and to eliminate seasonal effects. A sub-sample from the composite sample of litter is taken, oven dried and weighed to determine the dry weight. The dry to wet weight ratio of the sub-sample is calculated and used for estimations of the litter dry weight. To estimate the dry litter biomass in tonnes per hectar, the wet litter biomass for the composite sample plots is multiplied by the dry to wet weight ratio and an expansion factor for the plot size to calculate the litter biomass in tonnes per hectar (10,000 m2/(4 * area of sampling frame in m2)).  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 33) where:  EMBED Equation.3 Biomass of dry litter for plot sp, in stratum i, at monitor yeart; t d.m. ha1 EMBED Equation.3 Wet weight (field) of the litter in plot sp, of stratum i; kg  EMBED Equation.3 Dry-to-wet weight ratio of the litter (dry weight/wet weight); dimensionless EMBED Equation.3  Area of sampling frame for plot sp, in stratum i; m2i1, 2, 3, MPS strata in the project scenariospIndex for sample plotsCalculate the biomass of the litter (BLI,i,t in t d.m.) for each stratum applying approach used in Eq. REF _Ref226785321 \h  \* MERGEFORMAT (18) - i.e., Step7 of the BEF method and using litter specific data. The average annual change in the carbon stock of litter from the data at two monitoring intervals shall be calculated. As recommended in the Good Practice Guidance on LULUCF (Chapter 3.2, p3.35), the dry mass of litter is converted into carbon using 0.370 t C t-1 d.m. as a default value for the carbon fraction.  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 34) where:  EMBED Equation.3 Annual change in the litter carbon pool in stratum i (averaged over a monitoring period); t C yr1 EMBED Equation.3 Biomass of litter in stratum i at yeart; t d.m.TNumber of years between monitoring time t2 and t1 (T = t2 t1); yr EMBED Equation.3  Carbon fraction of litter (default value 0.370 t C t-1 d.m.); t C t-1 d.m.i1, 2, 3, MPS strata in the project scenariot 1, 2, 3, t* years elapsed since the start of the A/R CDM project activity5.1.5 Soil Organic Carbon (if selected in Table 1) For ex ante estimations, the changes in stocks of soil organic carbon may be assessed using the default method or the changes shall be conservatively neglected. For ex post estimations, the changes in stocks of soil organic carbon may be assessed using the default method as described below. 5.1.5.1 Default method A/R CDM project activities may account for changes in soil organic carbon pool using a default approach in areas of land included in their boundary which satisfy all conditions listed below: The area does not include organic soils (e.g., peat-lands), or wetlands; Removal of existing vegetation during site preparation for the A/R CDM project activity shall not occur on more than 10% of the area, unless it can be demonstrated that land clearance, e.g., by slash-and-burn activities, is a common practice in the region in which the project is located; Litter shall remain on site and not be removed; Ploughing/ripping/scarification associated with site preparation for planting, seeding and/or the human-induced promotion of natural seed sources, shall not exceed 10% of the project area (during each occasion); If ploughing/ripping/scarification is used for site preparation, it shall follow the land contour. If a part of an area of land included in the project boundary satisfies all conditions (i) - (v) listed above, the part shall be included in accounting of the default changes in the soil organic carbon pool. The default ex ante and ex post changes in the soil organic carbon pool  EMBED Equation.3  shall be estimated using the following equation:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 35) where:  EMBED Equation.3 Annual change in carbon stock in soil organic matter for area of landi, for yeart; tCyr-1AiArea of landi that satisfies all conditions (i)-(v) listed above; hectar (ha) EMBED Equation.3 Default annual increase in carbon stock in soil organic carbon; tC ha-1 yr-1tequilibriumTime until a new equilibrium in carbon stock in soil organic matter is reached in area of landi; years The default values of  EMBED Equation.3 =0.5 t C ha-1 yr-1 and tequilibrium =20 years shall be used. Changes in carbon stock in soil organic matter shall not be monitored ex post. 5.2 Estimation of GHG emissions within the project boundary The possible increase in GHG emissions as a result of the implementation of the proposed A/R CDM project activity within the project boundary is limited to burning of shrubs and trees of height lower than the threshold for height reported to EB according to paragraph8 of annex to Decision 5/CMP.1. If it occurs, it shall be estimated as:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 36) where:  EMBED Equation.3 Increase in GHG emissions as a result of the implementation of the proposed A/RCDM project activity within the project boundary; t CO2-e EMBED Equation.3 Non-CO2 emissions due to biomass burning of existing shrub vegetation as part of site preparation during the year t; t CO2-et 1, 2, 3, t* years elapsed since the start of the A/R CDM project activityNote: In this methodology Eq.  REF _Ref226785440 \h  \* MERGEFORMAT (33) is used to estimate the increase in GHG emissions for the period of time elapsed between project start(t =1) and the year t = t*, t* being the year for which actual net greenhouse gas removals by sinks are estimated. The monitoring of emissions by sources is only required if significant; if insignificant, evidence should be provided (e.g., as a relevant part of the monitoring of the project implementation) that the assumptions for the exclusion made in the exante assessment still hold in the expost situation. 5.2.1 Estimation of increase in non-CO2 emissions due to the project activities For the purpose of estimation of increase in non-CO2 emissions, shrubs and trees of height lower than the threshold for height reported to EB according to paragraph8 of annex to Decision 5/CMP.1 are treated as shrubs. The increase in non-CO2 emissions usually results from prescribed burning and it shall be calculated for each burnt area using the following approach:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 37) where:  EMBED Equation.3 Increase in non-CO2 greenhouse gas emissions due to biomass burning during site preparation; t CO2-eASBurnt area; ha EMBED Equation.3 Average above-ground biomass stock of shrub vegetation subject to burning; td.m.ha-1fBL,shrubAverage fraction of existing above-ground tree or shrub biomass (as indicated by subscripts in equations) left to decay after biomass burning; dimensionless. Default value derived from IPCC literature for shrub vegetation is: 0.05CFshrubAverage carbon fraction of biomass for trees or shrub vegetation (as indicated by subscripts in equations); t C (t d.m.)-1. IPCC default value for shrub vegetation is 0.49 EMBED Equation.3 Conversion factor: ratio of molecular weights of CH4 and C; mol mol-1ERCH4Emission ratio for CH4 (IPCC default: 0.012), kg C as CH4 (kg C burned)-1GWPCH4Global warming potential for CH4 (IPCC default: 21 for the first commitment period of the Kyoto Protocol); t CO2-e (t CH4)-1Leakage Under applicability conditions for this methodology, the land used for the project can under the proposed A/R CDM project activity continue to provide at least the same amount of goods and services. Consequently, as a result of the A/R CDM project activity, agricultural or pastoral activities will not be displaced from the project sites to other locations. Leakage shall be estimated as follows:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 38) where:  EMBED Equation.3 Total GHG emissions due to leakage; t CO2-eNet Anthropogenic GHG Removals by Sinks The net anthropogenic GHG removals by sinks is the actual net GHG removals by sinks minus the baseline net GHG removals by sinks minus leakage, therefore, the following general formula can be used to calculate the net anthropogenic GHG removals by sinks of an A/R CDM project activity(CAR-CDM), in tCO2-e.  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 39) where:  EMBED Equation.3  Net anthropogenic greenhouse gas removals by sinks; t CO2-e EMBED Equation.3 Actual net greenhouse gas removals by sinks; t CO2-e EMBED Equation.3 Baseline net greenhouse gas removals by sinks; t CO2-e EMBED Equation.3 Total GHG emissions due to leakage; t CO2-e7.1 Calculation of tCERs and lCERs To estimate the CERs that can be issued at yeart* = t2 (the date of verification) for the monitoring period T = t2 t1, this methodology uses the most recent version of the EB approved equations, which produces the same estimates as the following:  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 40)  EMBED Equation.3  ( SEQ "Equation"\* Arabic \* MERGEFORMAT 41) where:  EMBED Equation.3 Number of units of temporary Certified Emission Reductions EMBED Equation.3 Number of units of long-term Certified Emission Reductions EMBED Equation.3 Net anthropogenic greenhouse gas removals by sinks, as estimated for t* = t2; tCO2e EMBED Equation.3 Net anthropogenic greenhouse gas removals by sinks, as estimated for t* = t1; tCO2eData and parameters not monitored (default or possibly measured one time) In addition to the parameters listed in the tables below, the provisions on data and parameters not monitored in the tools referred to in this methodology apply. In choosing key parameters or making important assumptions based on information that is not specific to the project circumstances, such as in use of existing published data, PPs should retain a conservative approach: that is, if different values for a parameter are equally plausible, a value that does not lead to over-estimation of net anthropogenic GHG removals by sinks should be selected. Data / parameter:ABSL,iData unit:haUsed in equations: REF _Ref226787365 \h  \* MERGEFORMAT (4),  REF _Ref226787378 \h  \* MERGEFORMAT (9),  REF _Ref226787388 \h  \* MERGEFORMAT (11)Description:Area of baseline stratum iSource of data:GPS coordinates and/or remote sensing dataMeasurement procedures (if any):N/AAny comment: Data / parameter: EMBED Equation.3 Data unit:DimensionlessUsed in equations: REF _Ref226787404 \h  \* MERGEFORMAT (6)Description:Biomass expansion factor for conversion of annual net increment (including bark) in stem biomass to total above-ground tree biomass increment for speciesjSource of data:The source of data shall be either of the following: (a) Existing local and species-specific or group of species-specific; (b) National and species-specific or group of species-specific (e.g., from national GHG inventory); (c) Species-specific or group of species-specific from neighbouring countries with similar conditions; (d) Globally species-specific or group of species-specific (e.g., IPCC literature: Table 3A.1.10of the GPG-LULUCF (IPCC 2003), and Table4.5 of the AFOLU Guidelines (IPCC 2006).) Measurement procedures (if any):Any comment:BEFs in IPCC literature and national inventory data are usually applicable to closed canopy forest. If applied to individual trees growing in open field it is recommended that the selected BEF be increased by a further 30%.  Data / parameter: EMBED Equation.3  Data unit: DimensionlessUsed in equations: REF _Ref226787378 \h  \* MERGEFORMAT (9),  REF _Ref226787459 \h  \* MERGEFORMAT (15)Description:Biomass expansion factor for conversion of stem biomass to above-ground tree biomass for tree species jSource of data:The source of data shall be either of the following: (a) Existing local and species-specific or group of species-specific; (b) National and species-specific or group of species-specific (e.g., from national GHG inventory); (c) Species-specific or group of species-specific from neighbouring countries with similar conditions; (d) Globally species-specific or group of species-specific (e.g., IPCC GPG-LULUCF 2003).Measurement procedures (if any):Any comment:BEFs in IPCC literature and national inventory are usually applicable to closed canopy forest. If applied to individual trees growing in open field it is recommended that the selected BEF be increased by a further 30%.  Data / parameter: EMBED Equation.3 Data unit:t C t-1 d.m.Used in equations: REF _Ref226787515 \h  \* MERGEFORMAT (23),  REF _Ref226787530 \h  \* MERGEFORMAT (24)Description:Carbon fraction of biomass for planted non-tree woody vegetationSource of data:Default value 0.49 t C t-1 d.m. shall be usedMeasurement procedures (if any):Any comment: Data / parameter: EMBED Equation.3 Data unit:t C t-1 d.m.Used in equations: REF _Ref226787909 \h  \* MERGEFORMAT (30)Description:Carbon fraction of dry matter in dead wood Source of data:Default value 0.5 t C t-1 d.m. shall be usedMeasurement procedures (if any):Any comment: Data / parameter: EMBED Equation.3 Data unit:t C t-1 d.m.Used in equations: REF _Ref226787365 \h  \* MERGEFORMAT (4),  REF _Ref226787378 \h  \* MERGEFORMAT (9),  REF _Ref226787388 \h  \* MERGEFORMAT (11),  REF _Ref226787459 \h  \* MERGEFORMAT (15),  REF _Ref226787631 \h  \* MERGEFORMAT (19)Description:Carbon fraction of dry matter for species of type jSource of data:The source of data shall be either of the following: (a) National and species-specific or group of species-specific (e.g., from national GHG inventory); (b) Species-specific or group of species-specific from neighbouring countries with similar conditions; (c) Globally species-specific or group of species-specific (e.g., IPCCGPGLULUCF 2003); (d) The default IPCC value 0.5 t C t-1 d.m.Measurement procedures (if any):N/AAny comment: Data / parameter: EMBED Equation.3  Data unit:t C t-1 d.m.Used in equations: REF _Ref226787940 \h  \* MERGEFORMAT (34)Description:Carbon fraction of litter Source of data:Default value 0.37 t C t-1 d.m. shall be usedMeasurement procedures (if any):Any comment: Data / parameter: EMBED Equation.3 Data unit:t d.m. m-3Used in equations: REF _Ref226787404 \h  \* MERGEFORMAT (6),  REF _Ref226787378 \h  \* MERGEFORMAT (9),  REF _Ref226787459 \h  \* MERGEFORMAT (15), (23)Description:Basic wood density for species jSource of data:The source of data shall be either of the following: (a) National and species-specific or group of species-specific (e.g., from national GHG inventory); (b) Species-specific or group of species-specific from neighbouring countries with similar conditions; (c) Globally species-specific or group of species-specific (e.g., IPCC GPGLULUCF 2003).Measurement procedures (if any):N/AAny comment: Data / parameter: EMBED Equation.3 Data unit:t d.m. m-3Used in equations: REF _Ref226788046 \h  \* MERGEFORMAT (32)Description:Basic wood density of dead wood in the density state: 1 (sound), 2(intermediate) or 3 (rotten)Source of data:The source of data shall be either of the following: (a) National and species-specific or group of species-specific (e.g., from national GHG inventory); (b) Species-specific or group of species-specific from neighbouring countries with similar conditions; (c) Globally species-specific or group of species-specific (e.g., IPCC GPGLULUCF 2003).Measurement procedures (if any):Project specific determination of the density is allowedAny comment: Data / parameter:fj(DBH, H)Data unit:t d.m. tree1Used in equations: REF _Ref226787388 \h  \* MERGEFORMAT (11),  REF _Ref226787631 \h  \* MERGEFORMAT (19)Description:Allometric equation for species j linking diameter at breast height (DBH) and possibly tree height (H) to above-ground biomass of living treesSource of data:Whenever available, use allometric equations that are species-specific or group of species-specific, provided the equations have been derived using a wide range of diameters and heights, based on datasets that comprise at least 20 trees. Otherwise, default equations from IPCC literature, national inventory reports or published peer-reviewed studies may be usedsuch as those provided in Tables4.A.1 to 4.A.3 of the GPG-LULUCF (IPCC 2003).Measurement procedures (if any):Any comment:If default allometric equations are available for conditions that are similar to the project (same vegetation genus; same climate zone; similar forest type), then the equation may be used and considered conservative. Otherwise, it is necessary either to use conservatively assessed values, or to verify the applicability of the equation if mean predicted values are to be used. Allometric equations can be verified by: Selecting at least 5 trees covering the range of DBH existing in the project area, and felling and weighing the above-ground biomass to determine the total (wet) weight of the stem and branch components; Extracting and immediately weighing sub-samples from each of the wet stem and branch components, followed by oven drying at 70C to determine dry biomass; Determining the total dry weight of each tree from the wet weights and the averaged ratios of wet and dry weights of the stem and branch components. If the biomass of the harvested trees is within about 10% of the mean values predicted by the selected default allometric equation, and is not biasedor if biased is wrong on the conservative side (i.e., use of the equation results in an underestimate rather than overestimate of project net anthropogenic removals by sinks)then mean values from the default equation may be used. Data / parameter: EMBED Equation.3 ,  EMBED Equation.3 Data unit:t d.m. non-tree1, m3non-tree-1Used in equations: REF _Ref226787515 \h  \* MERGEFORMAT (23),  REF _Ref226787530 \h  \* MERGEFORMAT (24)Description:Allometric equation for species j linking diameter at at grid, breast or other height as appropriate (Dh), height (H), crown cover (CC), number of stems (NS) or other numerical data to above-ground biomass or volume of planted non-tree woody vegetation individual l of species j in plot sp in stratum i at yeart.Source of data:Whenever available, use allometric equations that are species-specific or group of species-specific, provided the equations have been derived using a wide range of diameters and heights, based on datasets that comprise at least 20 trees. Otherwise, default equations from IPCC literature, national inventory reports or published peer-reviewed studies may be used.Measurement procedures (if any):Any comment:If default allometric equations are available for conditions that are similar to the project (same vegetation genus; same climate zone), then the equation may be used and considered conservative. Otherwise, it is necessary either to use conservatively assessed values, or to verify the applicability of the equation if mean predicted values are to be used. Allometric equations can be verified by: Selecting at least 5 individuals covering the range of size existing in the project area, and felling and weighing the above-ground biomass to determine the total (wet) weight of the stem and branch components; Extracting and immediately weighing sub-samples followed by oven drying at 70C to determine dry biomass; Determining the total dry weight of each tree from the wet weights and the averaged ratios of wet and dry weights of the stem and branch components. If the biomass of the harvested individuals is within about 20% of the values predicted by the selected default allometric equation, and is not biasedor if biased is wrong on the conservative side (i.e., use of the equation results in an underestimate rather than overestimate of project net anthropogenic removals by sinks)then values from the default equation may be used. Data / parameter: EMBED Equation.3 Data unit:m3 ha-1 yr-1Used in equations: REF _Ref226787404 \h  \* MERGEFORMAT (6)Description:Average annual increment in stem volume of species j in stratum i, for yeartSource of data:Shall be based on national/local growth curve/table that usually used in national/local forest inventoryMeasurement procedures (if any):N/AAny comment:To be determined if the carbon gain-loss method is used in the estimation of carbon stock changes in above-ground and below-ground biomass in the baseline Note:  EMBED Equation.3 is estimated as the current annual increment CAI. The mean annual increment MAI in the forestry jargon can only be used if its use leads to conservative estimates. Note: The values read from tables if expressed on the per unit of area basis will usually apply to forest. Thus, they should be corrected to be applicable in the baseline conditions, e.g., by multiplication by the fraction of tree crown cover or fraction of number of stems in the baseline stratum of interest (other ways of correction may be proposed by project proponents). Data / parameter: EMBED Equation.3 Data unit:trees ha-1Used in equations: REF _Ref226787388 \h  \* MERGEFORMAT (11)Description:Pre-project tree stand density of species j in stratum i, at yeart Source of data:Field measurements (pre-project)Measurement procedures (if any):Tree counts on sample plots. These tree counts are used to estimate number of trees per hectar.Any comment: Data / parameter: EMBED Equation.3 Data unit:kg d.m.yr-1 (kg d.m.yr-1 )-1Used in equations: REF _Ref226788204 \h  \* MERGEFORMAT (10),  REF _Ref226788249 \h  \* MERGEFORMAT (16),  REF _Ref226788264 \h  \* MERGEFORMAT (20), (25)Description:Root-shoot ratio appropriate for biomass stock, for species jSource of data:The source of data shall be either of the following: (a) National and species-specific or group of species-specific (e.g., from national GHG inventory); (b) Species-specific or group of species-specific from neighbouring countries with similar conditions. Sometimes b) might be preferable to a); (c) Species-specific or group of species-specific from global studies.Measurement procedures (if any):N/AAny comment:For the purpose of estimating baseline removals by sinks, a conservative value is about one standard deviation (circa 0.04) above the mean (0.26); i.e., a value of 0.3 kg d.m. kg-1 d.m. For the purpose of estimating the project removals by sinks, use a value about one standard deviation below the mean; i.e., 0.22kgd.m.kg1d.m. Data / parameter: EMBED Equation.3 Data unit:kg d.m.yr-1 (kg d.m.yr-1 )-1Used in equations: REF _Ref226788288 \h  \* MERGEFORMAT (5)Description:Root-shoot ratio appropriate for biomass increment for species jSource of data:The source of data shall be either of the following: (a) National and species-specific or group of species-specific (e.g., from national GHG inventory); (b) Species-specific or group of species-specific from neighbouring countries with similar conditions. Sometimes b) might be preferable to a); (c) Species-specific or group of species-specific from global studies.Measurement procedures (if any):N/AAny comment:Conservative choice of default values: If in the sources of data mentioned above, default data are available for conditions that are similar to the project (same vegetation genus; same climate zone; similar forest type), then mean values of default data may be used and are considered conservative; Global values may be selected from Table 3A.1.8 of the GPG-LULUCF (IPCC 2003), or equivalently from Table 4.4 of the AFOLU Guidelines (IPCC 2006), by choosing a climatic zone and species that most closely matches the project circumstances.  Data / parameter: EMBED Equation.3 Data unit:m3 ha-1Used in equations: REF _Ref226787378 \h  \* MERGEFORMAT (9)Description:Pre-project tree stem volume of stratum i, species j, at yeartSource of data:Shall be estimated on the basis of number of trees and national/local growth curve/table that is usually covered by national/local forest inventoryMeasurement procedures (if any):Any comment:To be determined if the stock change method is used in the estimation of carbon stock changes in above-ground and below-ground biomass in the baseline. Note: The values read from tables if expressed on the per unit of area basis will usually apply to forest. Thus, they should be corrected to be applicable in the baseline conditions, e.g., by multiplication by the fraction of tree crown cover or fraction of number of stems in the baseline stratum of interest (other ways of correction may be proposed by PPs).  Data / parameter: EMBED Equation.3 Data unit:tC ha-1 yr-1Used in equations: REF _Ref226788333 \h  \* MERGEFORMAT (35)Description:Default annual increase in carbon stock in soil organic carbonSource of data:The default value of  EMBED Equation.3 =0.5 t C ha-1 yr-1 shall be used.Measurement procedures (if any):N/AAny comment: Data / parameter:tequilibriumData unit:yearsUsed in equations: REF _Ref226788333 \h  \* MERGEFORMAT (35)Description:Time until a new equilibrium in carbon stock in soil organic matter is reached Source of data:The default value of tequilibrium =20 years shall be usedMeasurement procedures (if any):N/AAny comment:III. MONITORING METHODOLOGY All data collected as part of monitoring should be archived electronically and be kept at least for 2years after the end of the last crediting period. One hundred percent of the data should be monitored if not indicated otherwise in the tables below. All measurements should be conducted according to relevant standards. In addition, the monitoring provisions in the tools referred to in this methodology apply. Monitoring of Project Implementation Information shall be provided, and recorded in the project design document (PDD), to establish that: The geographic position of the project boundary is recorded for all areas of land; The geographic coordinates of the project boundary (and any stratification inside the boundary) are established, recorded and archived. This can be achieved by field survey (e.g., using GPS), or by using georeferenced spatial data (e.g., maps, GIS datasets, orthorectified aerial photography or georeferenced remote sensing images). Commonly accepted principles of forest inventory and management are implemented: Standard operating procedures (SOPs) and quality control/quality assurance (QA/QC) procedures for forest inventory including field data collection and data management shall be applied. Use or adaptation of SOPs already applied in national forest monitoring, or available from published handbooks, or from the IPCC GPG LULUCF 2003, is recommended; Apply SOPs, especially, for actions likely to minimize soil erosion in those circumstances in which site preparation or planting involves soil disturbance capable to increase soil erosion above the baseline value; The forest planting and management plan, together with a record of the plan as actually implemented during the project shall be available for validation or verification, as appropriate. Sampling design and stratification Stratification of the project area into relatively homogeneous units can either increase the measuring precision without increasing the cost unduly, or reduce the cost without reducing measuring precision because of the lower variance within each homogeneous unit. PPs should present in the AR-CDM-PDD an exante stratification of the project area or justify the lack of it. The number and boundaries of the strata defined exante may change during the crediting period (expost). 2.1 Updating of strata The ex post stratification shall be updated because of the following reasons: Unexpected disturbances occurring during the crediting period (e.g., due to fire, pests or disease outbreaks), affecting differently various parts of an originally homogeneous stratum; Forest management activities (cleaning, planting, thinning, harvesting, coppicing, re-replanting) that are implemented in a way that affects the existing stratification. Established strata may be merged if reasons for their establishing have disappeared. 2.2 Sampling framework To determine the sample size and allocation among strata, this methodology uses the latest version of the tool for the Calculation of the number of sample plots for measurements within A/R CDM project activities, approved by the CDM Executive Board. The targeted precision level for biomass estimation within each stratum is 10% of the mean at a 95% confidence level. Data and parameters monitored The following parameters should be monitored during the project activity. When applying all relevant equations provided in this methodology for the exante calculation of net anthropogenic GHG removals by sinks, PPs shall provide transparent estimations for the parameters that are monitored during the crediting period. These estimates shall be based on measured or existing published data where possible and PPs should retain a conservative approach: that is, if different values for a parameter are equally plausible, a value that does not lead to over-estimation of net anthropogenic GHG removals by sinks should be selected. Data / parameter:AiData unit:haUsed in equations: REF _Ref226789082 \h  \* MERGEFORMAT (18),  REF _Ref226789093 \h  \* MERGEFORMAT (27),  REF _Ref226789103 \h  \* MERGEFORMAT (32),  REF _Ref226789114 \h  \* MERGEFORMAT (35)Description:Area of stratum iSource of data:Monitoring of strata and stand boundaries shall be done preferably using a Geographical Information System (GIS), which allows for integrating data from different sources (including GPS coordinates and Remote Sensing data).Measurement procedures (if any):Monitoring frequency:QA/QC procedures:Any comment: Data / parameter:ai,spData unit:m2Used in equations: REF _Ref226789142 \h  \* MERGEFORMAT (33)Description:Area of sampling frame for plot sp in stratum iSource of data:Simple measurement or manufacturers data Measurement procedures (if any):Once selected, the selected size of the sampling frame shall be fixed until the end of the last crediting period.Monitoring frequency:QA/QC procedures:Any comment:Sampling frame will be used to collect litter samples Data / parameter: EMBED Equation.3 Data unit:haUsed in equations: REF _Ref226789082 \h  \* MERGEFORMAT (18),  REF _Ref226789093 \h  \* MERGEFORMAT (27)Description:Total area of all sample plots in stratum iSource of data:Field measurementMeasurement procedures (if any):Monitoring frequency:QA/QC procedures:Any comment: Data / parameter: EMBED Equation.3 Data unit:kgUsed in equations: REF _Ref226789142 \h  \* MERGEFORMAT (33)Description:Humid weight (field) of the litter in plot sp of stratum iSource of data:Field measurements in sample plotsMeasurement procedures (if any):Step 1: Litter shall be sampled using a sampling frame. The frame is placed at four locations within the sample plot. Step 2: At each location, all litter (leaves, fruits, small wood, etc.) falling inside the frame shall be collected and the litter from four locations is mixed to get a representative sample for measuring the wet weight of the biomass.Monitoring frequency:QA/QC procedures:Any comment: Data / parameter: EMBED Equation.3 Data unit:cmUsed in equations: REF _Ref226789242 \h  \* MERGEFORMAT (31)Description:Diameter of piece n of dead wood along the transect in stratum i, at yeartSource of data:Field measurements in sample plotsMeasurement procedures (if any):Lying dead wood should be sampled using the line intersect method (Harmon and Sexton, 1996). Two 50-m lines bisecting each plot are established, and the diameters of the lying dead wood (e"5 cm diameter) intersecting the lines are measured.Monitoring frequency:QA/QC procedures:Any comment: Data / parameter:DBHData unit:cmUsed in equationsImplicitly used in Eqs.  REF _Ref226789265 \h  \* MERGEFORMAT (11),  REF _Ref226789272 \h  \* MERGEFORMAT (19)Description:Diameter breast height of treeSource of data:Field measurements in sample plotsMeasurement procedures (if any):Typically measured 1.3 m above-ground. Measure in the permanent sample plots all the trees above some minimum DBH that result from the A/R project activity. The minimum DBH varies depending on tree species and climate; for instance, the minimum DBH may be as small as 2.5 cm in arid environments where trees grow slowly, whereas it could be up to 10 cm for humid environments where trees grow rapidly.Monitoring frequency:QA/QC procedures:Any comment:Note: For ex ante estimations, mean DBH and H values should be estimated for tree speciesj in stratumi, at yeart using a growth model or yield table that gives the expected tree dimensions as a function of tree age.  Data / parameter:HData unit:mUsed in equations:Implicitly used in Eqs.  REF _Ref226789265 \h  \* MERGEFORMAT (11),  REF _Ref226789272 \h  \* MERGEFORMAT (19)Description:Height of treeSource of data:Field measurements in sample plotsMeasurement procedures (if any):Monitoring frequency:QA/QC procedures:Any comment:Note: For ex ante estimations, mean DBH and H values should be estimated for tree species j in stratum i, at yeart using a growth model or yield table that gives the expected tree dimensions as a function of tree age Data / parameter:LData unit:mUsed in equations: REF _Ref226789242 \h  \* MERGEFORMAT (31)Description:Length of the transect to determine volume of lying dead woodSource of data:Field measurementsMeasurement procedures (if any):Monitoring frequency:QA/QC procedures:Any comment: Data / parameter: EMBED Equation.3 Data unit:DimensionlessUsed in equations: REF _Ref226789142 \h  \* MERGEFORMAT (33)Description:Dry-to-wet weight ratio of the litter (dry weight/wet weight) Source of data:Laboratory measurement of field samplesMeasurement procedures (if any):Litter samples shall be collected and well mixed into one composite sample at the same time of year in order to account for natural and anthropogenic influences on the litter accumulation and to eliminate seasonal effects. A subsample from the composite sample of litter is taken, oven dried and weighed to determine the dry weight.Monitoring frequency:QA/QC procedures:Any comment: Data / parameter:NData unit:DimensionlessUsed in equations: REF _Ref226789242 \h  \* MERGEFORMAT (31)Description:Total number of wood pieces intersecting the transectSource of data:Field measurementsMeasurement procedures (if any):Monitoring frequency:QA/QC procedures:Any comment:Conservative Approach and Uncertainties To help reduce uncertainties in the accounting of emissions and removals, this methodology uses whenever possible the proven methods from the GPG-LULUCF, GPG-2000, and the IPCCs Revised 2006 Guidelines. As well, tools and guidance from the CDM Executive Board on conservative estimation of emissions and removals are also used. Despite this, potential uncertainties still arise from the choice of parameters to be used. Uncertainties arising from, for example, biomass expansion factors(BEFs) or wood density, would result in uncertainties in the estimation of both baseline net GHG removals by sinks and the actual net GHG removals by sinks - especially when global default values are used. It is recommended that PPs identify key parameters that would significantly influence the accuracy of estimates. Local values that are specific to the project circumstances should then be obtained for these key parameters, whenever possible. These values should be based on: Data from well-referenced peer-reviewed literature or other well-established published sources; or National inventory data or default data from IPCC literature that has, whenever possible and necessary, been checked for consistency against available local data specific to the project circumstances; or In the absence of the above sources of information, expert opinion may be used to assist with data selection. Experts will often provide a range of data, as well as a most probable value for the data. The rationale for selecting a particular data value should be briefly noted in the CDMARPDD. For any data provided by experts, the CDMAR-PDD shall also record the experts name, affiliation, and principal qualification as an expert (e.g., that they are a member of a countrys national forest inventory technical advisory group) as well as of a 1page summary CV for each expert consulted, included in an annex. In choosing key parameters or making important assumptions based on information that is not specific to the project circumstances, such as in use of default data, PPs should select values that will lead to an accurate estimation of net GHG removals by sinks, taking into account uncertainties. If uncertainty is significant, PPs should choose data such that it tends to under-estimate, rather than over-estimate, net GHG removals by sinks. References All references are quoted in footnotes. - - - - - History of the document VersionDateNature of revision05EB 47, Annex 12 28 May 2009Extended revision to apply the guidance provided in para 37 of the EB 44 report, including: Change in applicability conditions to avoid data intensive option for land use change in baseline and large leakage; Introduction of a default approach to assess changes in SOC; Reformatting according to the design applied in AR-ACM0001 (including unification of variables, equations and approaches).04EB 42, Para 35 26 September 2008Revisions mainly in the following sections: Section II. Baseline methodology 6.2 GHG emissions by sources 7 Leakage Section III. Monitoring Methodology 5.2 GHG emissions by sources 7 Leakage To apply the guidance provided in para 35, EB 42 meeting report regarding accounting of GHG emissions in A/R CDM project activities, from the following sources (i) fertilizer application, (ii) removal of herbaceous vegetation, and (iii) transportation. The Board agreed that emissions from these sources may be considered as insignificant.03EB 42, Annex 11 26September 2008 Allowing displacement of grazing activities, improvement of land use change approach, many editorial changes.02EB 36, Para 39 30November 2007Clarification to the application of the definition of the project boundary in A/R CDM project activities.01EB 29, Annex7 16February2007Initial adoption.  IPCC GPG-LULUCF 2003, Equation 3.2.2, Equation 3.2.4 and Equation 3.2.5.  This assumption implies that all baseline woody biomass is assumed to remain living and growing during the entire crediting period. This is conservative because the proportion of living biomass that will die or will be harvested is not deduced from the estimation of baseline net GHG removals by sinks and because the growth of the baseline biomass will cease (i.e., the biomass will reach saturation) at some point in time.  GPG-LULUCF Equation 3.2.3.  IPCC GPG-LULUCF 2003, Equation 3.2.3.  Harmon, M. E. and J. Sexton. (1996) Guidelines for Measurements of Woody Detritus in Forest Ecosystems. USLTER Publication No. 20. US LTER Network Office, University of Washington, Seattle, WA, USA.  Warren, W.G. and Olsen, P.F. (1964) A line transect technique for assessing logging waste, Forest Science 10:267276.  Van Wagner, C. E. (1968): The line intersect method in forest fuel sampling. Forest Science 14: 20-26.  Smith and Heath, 2002.  Wetlands, settlements, croplands and grasslands are land uses as defined in the Good Practice Guidance for Land Use, Land-use Change and Forestry (IPCC, 2003). Any woody perennial vegetation on settlements, croplands or grasslands must be below the thresholds for forestland.  Table 3A.1.15, Annex 3A.1, GPG-LULUCF (IPCC 2003).  See < HYPERLINK "http://cdm.unfccc.int/Reference/Guidclarif/" http://cdm.unfccc.int/Reference/Guidclarif/>.  Use the parameter BEF2 in Table 3A.1.10 in the GPG-LULUCF.  Values of the BEF must be derived from the parameter BCEFS in Table 4.5 (AFOLU guidelines, IPCC2006) according to the equation BEF = BCEFS /DV, using wood density.  Or, alternatively, seal the sub-samples immediately in plastic bags of known weight and determine wet weights in the laboratory.  Use at least 3 sub-samples for branch material and at least 5 sub-samples for stem wood. If cutting slices of stem or branch wood using a chainsaw, ensure cutting does not cause excessive heating and evaporation of water from the wood before the sub-sample is weighed.  W # 1 2 3 X Y \ Ͽϰxm[xNxG?Ghrhox#7 hrhox#hrh7{0JmH sH #jhrh7{UmH sH hrh7{mH sH jhrh7{UmH sH hrhV;jmH sH hrhox#mH sH hrhox#5\hrhox#CJhrhox#mH nHsH tHh#4hox#5mH nHsH tHhrhox#5mH nHsH tHhrhox#;mH nHsH tHhrhBd;mH nHsH tHW\  u Q%iw#$ & F ^` # & F! xgdM\# & F# & Fgd7{# & F ^`K$ $xa$ !$ & FxgdBdK~ &'(MNQ%iw QUb789:;ijk*3bŶ϶ϫϫ}re^W} hrh hrhhrhox#aJmH sH hrhSmH sH hrhTmH sH hrh+aJmH sH hrh+mH sH hrh= mH sH hrhox#mH sH hrhox#mH nHsH tHhrhox#5\ hrhox#hrhox#0Jj hrhFAU hrhV6jhrhox#U"wQ:k9CzL$$K 1$gdC# & F"gdylh & F"1$gd # & F pgdylh & F" 1$gdM\#$ & F # & F! xgdM\# & FJ=@sC˷˝ːąą|pcZPhrhox#5\hrhox#CJhrhox#CJnHtHhrhox#\mH sH hrhox#_HEhrhox#mH sH hrhaJmH sH hrhaJmH sH hrh'aJmH sH hrhV;jaJmH sH  hrhox#hrhox#aJmH sH hrh+aJ hrh+hrhSaJmH sH hrhSmH sH Cz;KLtz{<Vʼʜݎ||k|`TH?hrhox#@hrhox#\mH sH hrhox#5mH sH hrhox#mH sH !hrh'5\mHnHsH u#jhrhox#5U\mH sH hrhox#5\mH sH hrhox#0J\*jhrheCA>*B*U\phhrhx'>*B*\ph$jhrhx'>*B*U\phhrhox#\hrhox#\_HEhrhox#5CJ_HEnHtHt $$ $If$$$ $Ifa$$$$ $Ifa$$$xSD7- $If $ $Ifa$$ $Ifgdkd$$IflF # 7 ```06    4 lapVJd01Ap dy] , 5 !!骛鉁sasa#jhrhox#5U\mH sH hrhox#5\mH sH hrhox#\ hrhox#hrhox#mH sH hrhox#mH nH sH tH "hrhox#6]mH nH sH tH hrhV;j\mH sH hrhO\mH sH hrh\B\mH sH hrhox#@hrhox#\mH sH hrhox#nH tH !yl_U $If $ $Ifa$ $ $Ifa$kd$$IflF # 706    4 la0yl_U $If $ $Ifa$ $ $Ifa$kdH$$IflF # 706    4 laeyl_U $If $ $Ifa$ $ $Ifa$kd$$IflF # 706    4 laefyl_Y$If $ $Ifa$ $ $Ifa$kd$$IflF # 706    4 la ~!!!!!ytk`RRD$$$<$Ifa$$$$<$Ifa$ $$<$If$$x# & FkdI$$IflF # 706    4 la!!!!!'!+!~!!!!!!""X"Y"b"c"i"j"""""""""###óÛÔ~vlahrhox#nHtHhrhox#5\hrhox#\hrhox#H*hrhox#H*\mH sH  hrhox#hrhox#\mH sH hrhox#5mH sH hrhox#5mH nHsH tHhrhox#mH sH hrhox#5\mH sH #jhrhox#5U\mH sH !hrh'5\mHnHsH u!!!!!7//$ $<$Ifa$<$Ifkd$$IfH\ri e#2B ````(05$4 Hap(!"T"U"V"Z"c""LD<$Ifkd!$$IfH4\ri e#2B05$4 Haf4 $<$Ifa$ $<$Ifa$""""""bZOOD $<$Ifa$ $<$Ifa$<$Ifkd $$IfH4\ri e#2B05$4 Haf4""###$&bQL5LL#$$ & F ^`gdY # & F# & F e^e`kd $$IfH4\ri e#2B05$4 Haf4###5$9$Z$$&&F&H&I&''':';'ѵtgZP?1hrhox#6_HEnHtH!hrhox#5\]_HEnHtHhrhox#\]hrhPJnHtHhrhox#PJnHtHhrhox#PJ]nHtHhrhox#6PJnHtH!hrhox#5PJ\]nHtH hrhox#hrhox#_HEmH sH hrhox#nH tH hrhV;j_HEmH nHsH tH hrhox#_HEmH nHsH tHhrhox#5\&hrhox#5\aJmH nH sH tH &'(* +C+{+&,A--.?/F/_//y x$7$8$H$If$x$7$8$H$Ifgd\ U"# & Fgdn%#$ & F 85^5`# & F 85^5`#$ & F#$ & F ^`# & F# & F 5x^5`;'@'G'''( (((o)x)))))))))))** ***1*H*ȸq[q[qG'hrhox#\_HEaJmH nHsH tH*hrhox#6]_HEaJmH nHsH tH$hrhox#_HEaJmH nHsH tH"hrhox#6]mH nHsH tH%hrhox#6]mH nHo(sH tHhrhox#mH nHsH tHhrhox#mH nHo(sH tH hrhox#PJmH nHsH tHhrhox#\]hrhox#6]_HEnHtHhrhox#_HEnHtHH**++ +C+++++}-----..Y.Z.i... / /////ǼѼѼѼtbO$j hrhox#EHU\nH tH #j=`K hrhox#CJPJUVhrhox#\nH tH jhrhox#U\nH tH hrhNnH tH hrhV;j hrhn% hrhNhrh.nH tH hrhox#nH tH hrhox#5\ hrhox#hrhox#7aJnHtHhrhox#_HEnHtHhrhox#aJnHtH//:/;//?/E/F/G/H/[/\/]/^/////////źŋznc\J=cjfhrhox#EHU#j=`K hrhox#CJPJUV hrhox#jhrhox#Uhrhox#H*nH tH !j hrhox#EHUnH tH #jI hrhox#UVnH tH jhrhox#UnH tH  jDhrhox#nH tH hrhox#nHtHhrhox#nH tH hrhox#5hrh'5\mHnHuhrhox#5\jhrhox#5U\///009Skd$$IfF0+$ t644 la x$7$8$H$If$x$7$8$H$Ifgd\Skd$$IfF0+$ t644 la/000d000001111222222-2.2/202228292Ϳwm_m_P_mEhrhox#nHtHhrh'5\mHnHujhrhox#5U\hrhox#5\jhrhox#EHU3j-M hrhox#CJPJUVmH nHsH tHjhrhox#U hrhox#hrhox#6H*]nH tH hrhox#6]nH tH  jDhrhox#nH tH hrhox#5\nH tH hrhox#H*nH tH hrhox#nH tH 0d012292Q2222P3xSkd#$$IfF0!$ t644 la x$7$8$H$If#$ & F U" #$ & FgdJ $7$8$H$gd\ 92:2M2N2O2P22222222222<3?3C3D3E3F3G3M3O3Q3R3e3f3坖wl`N#jI hrhox#UVnH tH hrhox#H*nH tH hrh-cnH tH jhrhox#EHU#j=`K hrhox#CJPJUV hrhox#jhrhox#Uhrhox#H*nH tH hrhox#6]nH tH !jhrhox#EHUnH tH #j=`K hrhox#CJPJUVhrhox#nH tH jhrhox#UnH tH P3Q3i33333JSkd $$IfF0!$ t644 la x$7$8$H$IfSkd$$IfF0!$ t644 laf3g3h3i3u3v3333333 4 444$4&4(4)4*474844444ƷƩƚԎԎԂtƷfJf6jhrhox#0J5H*OJQJU\^JnH tH hrhox#5\nH tH  jDhrhox#nH tH hrhox#H*nH tH hrhox#H*nH tH hrhox#6H*]nH tH hrhn%6]nH tH hrhox#6H*]nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH !jhrhox#EHUnH tH 333'4(444JE; $7$8$H$# & FSkd$$IfF0!$ t644 la x$7$8$H$IfSkdi$$IfF0!$ t644 la444444444555555555/505152555Ѿ﷯}}r`Sr}Ehrhox#6]nH tH jhrhox#EHU#j=`K hrhox#CJPJUVjhrhox#Uhrhox#nH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5 hrhox#$j-hrhox#EHU\nH tH #j=`K hrhox#CJPJUVhrhox#\nH tH jhrhox#U\nH tH 455355556Lkd!$$Ifl02$64 la$x$7$8$H$Ifx$7$8$H$Ifgd\#$ & F U"55555555555555&6'62636;6=6>6B6D666666666777ꯞꀋnaUhrhox#]nH tH j$hrhox#EHU#j<`K hrhox#CJPJUVjhrhox#U hrhox#hrhox#>*nH tH !jR"hrhox#EHUnH tH #j<`K hrhox#CJPJUVjhrhox#UnH tH hrhox#H*nH tH hrhox#6]nH tH hrhox#nH tH hrh-cnH tH !666,77777>Lkd )$$Ifl02$64 la $7$8$H$If x$7$8$H$If$x$7$8$H$Ifgd\Lkdm$$$Ifl02$64 la777 7!7)7+7,707O7P7c7d7e7f77777777777q_Nq!jk)hrhox#EHUnH tH #jI hrhox#UVnH tH jhrhox#UnH tH $jhrhox#0JH*UnH tH j&hrhox#EHU#j6cK hrhox#CJPJUV hrhox#jhrhox#Uhrhox#>*nH tH hrhox#H*nH tH hrh'nH tH hrhox#6]nH tH hrhox#nH tH 7777777777'8(8)8<8=8>8?8@8A8B8j8k8l8m8n8׳פ咁xpbXbIbphrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5hrhox#CJ!j,hrhox#EHUnH tH #jcK hrhox#CJPJUVjhrhox#UnH tH hrhox#6H*]nH tH hrhn%6]nH tH hrhox#hrhox#6]nH tH hrhox#nH tH hrhox#6H*]nH tH 777'8(8o8v888ZRK#$ & F U"Lkd+$$Ifl02$64 la x$7$8$H$IfLkdY+$$Ifl02$64 lan8o8v8w8888888888888999 9#9$9*9+9>9?9@9A9B999saPӢ!j3hrhox#EHUnH tH #j=`K hrhox#CJPJUV!jl1hrhox#EHUnH tH #jcK hrhox#CJPJUVhrhox#H*nH tH hrhox#6]nH tH !j.hrhox#EHUnH tH #j<`K hrhox#CJPJUVjhrhox#UnH tH hrhox#nH tH #hrhox#OJQJ\^JnH tH 88 9)9*9B99TOkd|3$$Ifl40+$64 laf4 x$7$8$H$IfOkd1$$Ifl40+$64 laf49999999999999999::::#:1:2:T:b::::::::::ꯠܑ܂hW!j9hrhn%EHUnH tH 3jnM hrhn%CJPJUVmH nHsH tHhrhox#6H*]nH tH hrhox#6H*]nH tH jT6hrhox#UnH tH #jJ hrhox#UVnH tH jhrhox#UnH tH hrhox#H*nH tH hrhox#6]nH tH hrhox#nH tH hrh-cnH tH !999":#:%:S:JSkdD8$$IfF0+$ t644 la x$7$8$H$IfSkd5$$IfF0+$ t644 laS:T:V:::::JSkd9$$IfF0+$ t644 la x$7$8$H$IfSkd8$$IfF0+$ t644 la:::$;k;s;;;| x$7$8$H$If$x$7$8$H$If#$ & F U"# & FSkdm9$$IfF0+$ t644 la::::; ;!;";#;$;%;8;9;:;;;<;=;>;f;g;h;i;j;k;s;t;;;;;;;پ񾤯q`Rhrhox#6]nH tH !j>hrhox#EHUnH tH #jX=`K hrhox#CJPJUV!jq<hrhox#EHUnH tH j_K hrhox#PJUVhrhox#nH tH jhrhox#UnH tH hrhox#\nH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5 hrhox#;;;;;;;;;;;;<<<<_<a<b<c<n<o<z<{<<<<<<<<<<<<<<<<<걠ܒ܇ud!jChrhox#EHUnH tH #jNyL hrhox#CJPJUVhrhJnH tH hrh-c6]nH tH !jvAhrhox#EHUnH tH j_K hrhox#PJUVjhrhox#UnH tH hrhox#H*nH tH hrhox#6]nH tH hrhox#nH tH hrh-cnH tH ';;<<<<<TOkdC$$Ifl40+$64 laf4 x$7$8$H$IfOkdA$$Ifl40+$64 laf4<<=i==K>0x$7$8$H$If^`0 $7$8$H$Ifgdr x$7$8$H$IfOkdE$$Ifl40+$64 laf4< ====>=@=A=B=M=N=Y=Z=]=^=a=c=f=h=i=m=o=p========>>>G>H>L>M>`>a>b>ud!jJhrhox#EHUnH tH jJ hrhox#UV!jKHhrhox#EHUnH tH hrhox#>*nH tH hrhox#H*nH tH hrh-cnH tH hrhox#6]nH tH jhrhox#UnH tH !j@Fhrhox#EHUnH tH j_K hrhox#PJUVhrhox#nH tH 'K>L>d>>>>Y?TOkdL$$Ifl40+$64 laf4 x$7$8$H$IfOkdVJ$$Ifl40+$64 laf4b>c>>>>>>>>>>>C?D?E?V?X?Z?h?i??????@@@@@@@@@A屠׆we^W hrhox# hrh'#jPhrhox#UnH tH hrhox#6H*]nH tH hrhox#6H*]nH tH hrhJnH tH !jMhrhn%EHUnH tH 3jtnM hrhn%CJPJUVmH nHsH tHhrhox#H*nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH "Y?Z?\?????TOkdO$$Ifl40+$64 laf4 x$7$8$H$IfOkd(O$$Ifl40+$64 laf4???@@9BKDTJE# & F #$ & Fgd\OkdfP$$Ifl40+$64 laf4 x$7$8$H$IfOkdO$$Ifl40+$64 laf4AA#A$A.A0A1A2AEAFAGAHA`AcAAAAAAAAAAABBBB}B~BBBBBBBBB̿{c/j2_K hrhox#PJUVmH nH sH tH  hrh'jsUhrhox#UjVShrhox#EHU3j=`K hrhox#CJPJUVmH nH sH tH hrhox#>*jKQhrhox#EHU/j(_K hrhox#PJUVmH nH sH tH jhrhox#U hrhox#hrhox#6]%BBBBBBBBCCC4C5CHCICJCKCKDiDjDkDlDDDྱ|`|N|<#jLL hrhox#CJPJUV#jhrhox#5U\nH tH 6jhrhox#0J5H*OJQJU\^JnH tH hrhox#5\nH tH jZhrhox#EHU3j=`K hrhox#CJPJUVmH nH sH tH jWhrhox#EHU3j=`K hrhox#CJPJUVmH nH sH tH hrhox#>* hrhox#jhrhox#UjUhrhox#EHUKDkDDD@EEEEFF*FFtSkdGi$$IfF0$ t644 la x$7$8$H$If$x$7$8$H$Ifgd\#$ & F U" $7$8$H$ DDDDDDDDDDDDDDDDDDDDDDDDDD EEʼٕqʼeٕS#j.cK hrhox#CJPJUVhrhox#\nH tH 'j4_hrhox#5EHU\nH tH jU_K hrhox#PJUVhrhox#5\nH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5 hrhox##jhrhox#5U\nH tH 'j8\hrhox#5EHU\nH tH EEEEEE;EE?E@EAETEUEVEWEXEYEZEEEEEEEEEEʼʗىyeʼʗZKZjhrhox#UnH tH hrhox#nH tH 'jdhrhox#5EHU\nH tH j_K hrhox#PJUVhrhox#5\nH tH hrhox#\nH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5 hrhox##jhrhox#5U\nH tH 'jahrhox#5EHU\nH tH EEEEEEFFFFFFFF&F'F(F)FbFdFeFfFqFrFFFFFFFF´©´…t´i´©W#j&I hrhox#UVnH tH hrh-cnH tH !jihrhox#EHUnH tH /j?M hrhox#CJUVmH nHsH tHhrhox#H*nH tH hrh'nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH !j ghrhox#EHUnH tH #j6cK hrhox#CJPJUVFFFFFFAGJSkdn$$IfF0$ t644 la x$7$8$H$IfSkdk$$IfF0$ t644 laFFFFFFFFFFFFFFFF!G"G#G/G0G5G:G;GBGCGVGWGXGYGGGGȹȹ֩ȍւraShrh-c6]nH tH !jphrhox#EHUnH tH j_K hrhox#PJUVhrh'nH tH hrh-cnH tH !jdnhrhox#EHUnH tH j_K hrhox#PJUVhrhox#6H*]nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH jlhrhox#UnH tH AGBGZGGGGGJSkds$$IfF0$ t644 la x$7$8$H$IfSkdp$$IfF0$ t644 laGGGGGGGGGGGGGGGGGGGG)H*H4H6H:H?H@HAHBHCHDHGHIHKHLH_H}qcqchrhox#H*]nH tH hrhox#]nH tH hrhox#6nH tH !juhrhox#EHUnH tH j_K hrhox#PJUV!j_shrhox#EHUnH tH #j^cK hrhox#CJPJUVjhrhox#UnH tH hrh'nH tH hrhox#6]nH tH hrhox#nH tH #GGHJHKHcHHJSkdw$$IfF0$ t644 la x$7$8$H$IfSkdZu$$IfF0$ t644 la_H`HaHbHHHHHHHHHHHIIII"I#I6I7I8I9IdIeIlInIuIvIIIƸƬƞƸƬnƸƬ`jJ hrhox#UV!j|hrhox#EHUnH tH jJ hrhox#UV!jvzhrhox#EHUnH tH jJ hrhox#UVhrhox#H*nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH !j(xhrhox#EHUnH tH jJ hrhox#UVHHH!I"I:ItIJSkd|$$IfF0$ t644 la x$7$8$H$IfSkdz$$IfF0$ t644 latIuIIIIIJJSkd$$IfF0$ t644 la x$7$8$H$IfSkd~$$IfF0$ t644 laIIIIIIIIIIIJJ>JLJMJJJJJJJJJJJJJJԺƫƜԄsaPI hrhox#!jhrhox#EHUnH tH #jkcK hrhox#CJPJUV!jhrhox#EHUnH tH /j_K hrhox#PJUVmH nH sH tH hrhox#6H*]nH tH hrhox#6H*]nH tH hrhox#H*nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH !j/hrhox#EHUnH tH JJ J=J>J@JJJSkd$$IfF0$ t644 la x$7$8$H$IfSkd~$$IfF0$ t644 laJJJ.K6KNKK x$7$8$H$If U"#$ & FSkdB$$IfF0$ t644 laJJK(K)K+K,K-K.K6K7KJKKKLKMKKKKKKKKKKKKKKĹ{p{e{pS#jvcK hrhox#CJPJUVhrh'nH tH hrh-cnH tH hrhox#6]nH tH !jhrhox#EHUnH tH j_K hrhox#PJUVjhrhox#UnH tH hrhox#nH tH hrhox#\nH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5KKKKKKELFUkd$$$IfF_0$ t644 la x$7$8$H$IfUkdƉ$$IfFn0$ t644 laKKKKKKKKKKKLL L,L-L2L7L8LBLDLELFLGLZL[L\L]LLLLLLԶƗԌԀtbSԀjhrhox#UnH tH #jJ hrhox#UVnH tH hrhox#]nH tH hrhox#H*nH tH hrh'nH tH hrh-c6]nH tH !jhrhox#EHUnH tH j_K hrhox#PJUVhrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH !j)hrhox#EHUnH tH ELFL^LLLLF5$x$7$8$H$Ifgd-cUkd$$IfF}0$ t644 la x$7$8$H$IfUkd$$IfFn0$ t644 laLLLLLLLLLLMM(MGMIMMMcMfMXNfNgNNNNNN1O2OEOFOGOHOPP嶐嶁q`Y hrhox#!jhrhox#EHUnH tH j_K hrhox#PJUVhrhox#6H*]nH tH hrhox#6H*]nH tH hrhox#>*nH tH hrhrnH tH hrhox#6]nH tH jDhrhox#UnH tH #j7K hrhox#UVnH tH hrhox#nH tH jhrhox#UnH tH !LHMWNXNZNN x$7$8$H$IfUkd|$$IfF}0$ t644 la $7$8$H$Ifx$7$8$H$IfgdrNNNNNN OFUkdB$$IfF}0$ t644 la x$7$8$H$IfUkdߓ$$IfF}0$ t644 la OO6QgQ2RJRATbTTUWW}kc U"# & F 85^5`#$ & F ^` #$ & Fgd\ $7$8$H$# & FUkd$$IfF}0$ t644 la PP%P&P'P(P6QgQRR2R3RFRGRHRIRJRNRXRATPTXTbTTTTU\VnV휐zg]]Rhrh.nH tH hrhox#5\$j5hrhox#EHU\nH tH +j>K hrhox#UVmH nH sH tH hrhox#\nH tH jhrhox#U\nH tH hrhox#nH tH hrhox#5\nH tH jhrhox#EHU3jcK hrhox#CJPJUVmH nH sH tH  hrhox#jhrhox#UnVuVWWWWWWWWWWWWWWWWWWXXXX6X7X;X*nH tH jshrhox#UnH tH #j"I hrhox#UVnH tH hrhox#hrhox#H*nH tH jhrhox#UnH tH jhrhox#UnH tH #js'J hrhox#UVnH tH hrhox#nH tH XXYYY[G[JE; $7$8$H$# & FSkd|$$IfF0$ t644 la x$7$8$H$IfSkd$$IfF0$ t644 laiZjZmZnZoZ[G[\\\\%\&\'\(\)\*\+\S\T\V\W\Y\_\`\a\t\׺׫בvn``Q`nJ hrhox#hrh'5\mHnHujhrhox#5U\hrhox#5hrhox#6]!jXhrhox#EHUnH tH 3j^.M hrhox#CJPJUVmH nHsH tHjhrhox#UnH tH $jhrhox#0JH*UnH tH hrhox#5\hrhox#nH tH hrhox#6]nH tH hrhox#6H*]nH tH G[\Y\`\x\]].]~]Okd$$Ifl40$64 laf4 x$7$8$H$If $x7$8$H$gdY  U"# & Ft\u\v\w\]]]]*]+],]-]r]s]{]}]]]]]]]] ^^^"^&^(^*^ĸĦĉ}ĉo`ĸĸ}VLhrhox#6] jDhrhox#hrhox#6H*]nH tH hrhs6]nH tH hrhox#H*nH tH hrhox#6]nH tH j|hrhox#UnH tH #jJ hrhox#UVnH tH hrhox#H*nH tH hrhox#nH tH jhrhox#UnH tH jhrhox#UnH tH #jڀXJ hrhox#UVnH tH ~]]]]]]$^COkd$$Ifl40$64 laf4 x$7$8$H$If$x$7$8$H$IfgdnHOkd|$$Ifl40$64 laf4$^&^^ _._6___@Skd$$IfF0$ t644 la x$7$8$H$If U"#$ & FOkdL$$Ifl40$64 laf4*^,^^^^^^^^^^_____ _0_2_4_________sdsXsIjhrhox#UnH tH hrhox#H*nH tH hrhox#6H*]nH tH hrhox#6]nH tH hrhox#nH tH hrhox#\nH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5jhrhox#EHUj5 K hrhox#UVjhrhox#U hrhox#hrhox#6H*]____C`D`y`{`}`~```````aaaa+a,a-a.aeafaaaaaaaĶĪĘĶĪwhĶĪV#j5 K hrhox#UVnH tH jDhrhox#UnH tH #j5 K hrhox#UVnH tH jdzhrhox#UnH tH #j5 K hrhox#UVnH tH hrhox#H*nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH jJhrhox#UnH tH #j5 K hrhox#UVnH tH __|`}``aa/aaJSkd$$IfF0$ t644 laSkdh$$IfF0$ t644 la x$7$8$H$Ifaaa%b&b>bbJSkd޺$$IfF0$ t644 la x$7$8$H$IfSkdb$$IfF0$ t644 laaaaaa"b$b%b&b'b:b;bo]o_o`olomonorowoxooooooooooɶ~shaQBhjhrhox#EHUo(j_K hrhox#PJUV hrhox#jhrhox#Uhrh'nH tH hrhh6]nHtHhrhox#6]nHtHhrhh6]nH tH hrhox#6]nH tH $j4hrhox#EHUnH o(tH jijIK hrhox#UVjhrhox#UnH tH hrhox#mHnHsHtHhrhox#nH tH #o*o?ooooooFPkd$$Ifl0f$644 laPkdH$$Ifl0f$644 la x$7$8$H$If $7$8$H$oooooooooooooooopppp:pBpCpDpPpQpRp[p]p^pjpkplpppupvp|p}p~pp˽˽˽˽˽tjhrhox#UnH tH j/hrhox#EHUj_K hrhox#PJUVjhrhox#U hrhox#hrh'nH tH hrhh6]nH tH hrhox#6]nH tH hrhh6]nHtHhrhox#6]nHtHhrhox#nH tH 'op|p}ppppp?Pkd$$Ifl0f$644 laPkdg$$Ifl0f$644 la x$7$8$H$If$x$7$8$H$IfgdY ppppppppppppppppppppppp q q-q.qqdqeqtquqqqqqqq´´´‰´‰z‰z‰k‰aahrhox#5\hrhox#6H*]nH tH hrhox#6H*]nH tH hrhox#hrh'nH tH hrhhnH tH hrhh6]nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH $jhrhlxEHUnH o(tH j&_K hrhox#PJUV&pppp-q.q0qdqPPkd|$$Ifl0f$644 laPkd#$$Ifl0f$644 la x$7$8$H$IfdqeqhqqqqDrKrPIAI U"#$ & FPkd.$$Ifl0f$644 la x$7$8$H$IfPkd$$Ifl0f$644 laqqrrrrrrrr>r?rArBrCrDrIrKrLr\r]r^r_rrrrrrrrrr轵赽~l^S^hrh'nH tH hrhox#6]nH tH "jVhrhox#5EHU\o(j'IK hrhox#UVhrhox#mHnHsHtHhrhox#nH tH hrh'5\mHnHuhrhox#5 hrhox#"jhrhox#5EHU\o(#jL hrhox#CJPJUVjhrhox#5U\hrhox#5\Kr`rrrrrrsBPkd$$Ifl0f$644 laPkd]$$Ifl0f$644 la x$7$8$H$If$x$7$8$H$Ifrrrrrrrrrrrrrrrrrss,s-s2s3s4s5s6sFsGsLsMs\s]svswssƸƸƟƘwfƸƘWƸƘWƸhrhox#6H*]nH tH !j#hrhox#EHUnH tH #jL hrhox#CJPJUVjhrhox#UnH tH hrhox#hrh'nH tH hrhh6]nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#5U\"jhrhox#5EHU\o(j,IK hrhox#UV"s2s3s6sLsMsPssPPkdi$$Ifl0f$644 laPkd $$Ifl0f$644 la x$7$8$H$IfsssssstPPkd$$Ifl0f$644 la x$7$8$H$IfPkd$$Ifl0f$644 lasssssssstt$t%t,t-tItLtUt\t]tdttttuuuuNuwgZMZMgMMhrhox#_HEnHtHhrhox#_HEmH sH hrhox#5\_HEnHtHhrhox#6]_HEhrhox#_HEhrhox#5\_HEmH sH hrhox#5\_HEhrhox#5\]_HEhrhox#5\]aJhrhox#6H*]nH tH hrhox#nH tH hrhox#6H*]nH tH hrhox#6]nH tH hrhox#tt%tUttvdvkvvv x$7$8$H$If $ $ U"# & F $7$8$H$Pkdt$$Ifl0f$644 la NuOu[u\uuuuuvv0v1v2v3v4v5v6v^v_vavbvdvjvkvlvvvóÞwo_OjK_K hrhox#PJUVhrhox#\_HEnHo(tHhrhox#\hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5jhrhox#EHUjB_K hrhox#PJUV hrhox#jhrhox#Uhrhox#_HEnHo(tHhrhox#_HEnHtHhrhox#6]_HEnHtHvvvvvvvvvvvvvvvvvvvwwww;w}B}G}H}N}O}]}_}}}}}}}}õٮٵxٵxٵxõٮiٮiٮhrhox#6H*]nH tH hrhh6]nH tH j hrhox#EHUj_K hrhox#PJUVjhrhox#U hrhox#hrhox#6]nH tH hrh'nH tH hrhhnH tH hrhox#nH tH hrhh6]nHtHhrh r6]nHtH%||N}O}Q}}}}}VNkd~$$Ifl0$644 laNkd*$$Ifl0$644 la x$7$8$H$If}}}~~~~.VQQI U"# & FNkd&$$Ifl0$644 la x$7$8$H$IfNkd$$Ifl0$644 la}}~~ ~~~~~\~]~s~t~~~~~~~~~~~~~~~~~~ξ޴ީޛީΉ{i\Njhrhox#5U\jhrhox#EHU#jL hrhox#CJPJUVhrhox#6]nH tH hrhox#6\] hrh'jzhrhox#Ujhrhox#Uhrhox#5\hrhox#5\_HEmH sH hrhox#\hrhox#5 hrhox#hrhox#nH tH hrhox#6H*]nH tH ()+,-.56IJKL  ʿucTujPhrhox#UnH tH #j5 K hrhox#UVnH tH hrhox#H*nH tH hrhox#6]nH tH jhrhox#UnH tH #j5 K hrhox#UVnH tH jhrhox#UnH tH hrhox#nH tH hrhox#hrhox#5hrh'5\mHnHujhrhox#5U\hrhox#5\.5MCSkdn$$IfF0$ t644 laSkd$$IfF0$ t644 la x$7$8$H$If#$ & F !"#EFKPQYZmnopĀƀƸƭƛtƸhƸhƸƸhƸhƸYƸhrhox#6H*]nH tH hrhox#H*nH tH #j3hrhox#6U]nH tH )j],J hrhox#6UV]nH tH #jhrhox#6U]nH tH hrh'nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#5U\"jhrhox#5EHU\o(j'IK hrhox#UV!$XYqJSkd$$IfF0$ t644 laSkd$$IfF0$ t644 la x$7$8$H$If67J@;# & F $7$8$H$Skd$$IfF0$ t644 la x$7$8$H$IfSkdo$$IfF0$ t644 la7$NUZ[ip .0ĄTU]jvwąŅNȻȻؓػȻػػxhrhs_HEmH sH hrhox#_HEmH o(sH hrhox#]aJhrhox#]aJmH sH hrhox#6]_HEmH sH hrhox#_HEmH sH hrhox#5\_HEmH sH hrhox#5\]aJhrhox#nH tH hrhox#6H*]nH tH /Uz‡Ɉ@XgLkd($$Ifl0 $z64 la x$7$8$H$If#$ & F U"# & Fgds U"gd# & F Nnoq†͆ Y`z{²ҫj[MCMhrh5\jhrh5U\j-hrhox#EHUaJ3jM hrhox#CJPJUVmH nHsH tHhrhox#aJjhrhox#UaJ hrhox#OJQJ^JnH tH hrhox#hrhJ5\_HEmH sH hrhox#5\_HEmH sH hrhox#_HEmH sH hrhox#_HEhrhox#5\]aJhrhox#]aJ‡ˇ҇߇)+2ÈĈƈLjȈɈeVHHHjhrhox#5U\j@"hrhox#EHUaJ3jˢM hrhox#CJPJUVmH nHsH tHhrhox#aJjhrhox#UaJ hrhox#hrhox#5\]aJhrhox#]aJhrhox#_HEmH sH hrhox#5\_HEmH sH hrhox#5hrhox#5\jhrh5U\hrh'5\mHnHuɈ؈و&'78<=>@ATUVWXڻڻj]I&hrhox#6OJQJ]^JnH tH j9&hrhox#EHU/j|M hrhox#CJUVmH nHsH tH hrhox#jhrhox#Uhrhox#mH nHsH tH/j%hrhox#OJQJU^JnH tH hrh'/j?%hrhox#OJQJU^JnH tH )jhrhox#OJQJU^JnH tH hrhox#OJQJ^JnH tH ʉ̉ЉՉ։Վ|jcXc>3jߢM hrhox#CJPJUVmH nHsH tHjhrhox#U hrhox##hrhox#H*OJQJ^JnH tH #hrhhH*OJQJ^JnH tH hrh|UOJQJ^JnH tH hrh'OJQJ^JnH tH hrhox#OJQJ^JnH tH &hrhh6OJQJ]^JnH tH &hrhox#6OJQJ]^JnH tH hrhox#]aJhrhox#_HEmH sH  !"-./;<=FHIUVW[`adeghi|µӊӊӊӊyg`` hrhox##hrhox#H*OJQJ^JnH tH hrh'OJQJ^JnH tH &hrhh6OJQJ]^JnH tH hrhox#5\]aJhrhox#]aJhrhox#_HEmH sH  hrhox#OJQJ^JnH tH &hrhox#6OJQJ]^JnH tH jhrhox#Uj )hrhox#EHUgh@ZLkd.$$Ifl0 $z64 la x$7$8$H$IfLkd+$$Ifl0 $z64 la|}~ƊȊɊՊ֊׊ۊƵvvvbvQƊ hrh'OJQJ^JnH tH &hrh r6OJQJ]^JnH tH &hrhh6OJQJ]^JnH tH &hrhox#6OJQJ]^JnH tH hrhox#]aJhrhox#_HEmH sH  hrhox#OJQJ^JnH tH hrhox#jhrhox#Uj ,hrhox#EHU3j좀M hrhox#CJPJUVmH nHsH tH&'23=?@AEdeӋԋ ŸŏňŸŏwŏlŸň^hrhox#6]nH tH hrhox#mH sH  hrh|UOJQJ^JnH tH hrhox##hrhox#H*OJQJ^JnH tH hrhox#5\]aJhrhox#]aJhrhox#_HEmH sH  hrhox#OJQJ^JnH tH &hrhox#6OJQJ]^JnH tH )hrhox#6H*OJQJ]^JnH tH @AE ZI$x$7$8$H$IfgdY Lkd_/$$Ifl0 $z64 la x$7$8$H$IfLkd.$$Ifl0 $z64 la >?AuILkd#0$$Ifl0 $z64 la x$7$8$H$If$x$7$8$H$IfgdhLkd/$$Ifl0 $z64 la>?MOuvŌƌˌ̌ΌKL_`abcde޷ޢފ}rddUdMhrhox#5hrh'5\mHnHujhrhox#5U\hrhox#6H*]jI1hrhox#EHU/j|M hrhox#CJUVmH nHsH tHjhrhox#Uhrh-5\hrhox#5\hrhox#6H*]nH tH hrhox#6]nH tH hrhox#hrhox#nH tH hrhox#6H*]nH tH uvyŌƌKZPHA#$ & F U" #$ & FgdylhLkd0$$Ifl0 $z64 la x$7$8$H$IfLkd0$$Ifl0 $z64 la׍ڍۍ $%&*/0578KLMNOwxh[j7hrhox#EHU/j&}M hrhox#CJUVmH nHsH tHhrh'nH tH hrhh6]nH tH hrhox#6]nH tH hrhox#]aJhrhox#_HEmH sH hrhox#nH tH j/4hrhox#EHU/j/}M hrhox#CJUVmH nHsH tHjhrhox#U hrhox##67OӎԎ@Ukdt9$IfK$L$F0U$ t$644 laUkd6$IfK$L$F0U$ t$644 la x$IfK$ $x$IfK$ŽÎǎ͎̎ҎԎՎ?MN^_afgٹ|rg]Shrh-5\hrhox#5\hrhox#B*phhrhox#6]hrhox#]aJhrhox#_HEmH sH j9hrhox#EHUj&AK hrhox#UVjhrhox#U hrhox#hrh'nH tH hrh r6]nH tH hrhox#nH tH hrhh6]nH tH hrhox#6]nH tH ^_`aM83# & F`kd<$$IflU%$0$64 lax$IfUkd;$IfK$L$F0U$ t$644 la x$IfK$giƏɏԏ֏ُޏ 67HJKLMN^_`acd髜鎄uj[hrhox#mHnHsHtHhrhox#nH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\j<hrhox#EHUo(/j~M hrhox#CJUVmH nHsH tHjhrhox#Uhrhylh6] hrh'hrhox#6] hrhox#hrhox#5\_HEmH sH !M PkdB$$Ifl0>$644 la x$7$8$H$If $7$8$H$ U" ͺ季啇yk`yUN hrhox#jhrhox#Uhrh'nH tH hrhh6]nHtHhrhox#6]nHtHhrhh6]nH tH hrhox#6]nH tH hrhox#]aJhrhox#_HEmH sH $jD@hrhox#EHUnH o(tH /j|M hrhox#CJUVmH nHsH tHhrhox#nH tH jhrhox#UnH tH HIjklxyzµsshaaI/j|M hrhox#CJUVmH nHsH tH hrhox#hrh'nH tH hrhh6]nHtHhrhox#6]nHtHhrhh6]nH tH hrhox#6]nH tH hrhox#]aJhrhox#_HEmH sH hrhox#nH tH jhrhox#UjBhrhox#EHUo(/j|M hrhox#CJUVmH nHsH tH@AVPPkd4H$$Ifl0>$644 la x$7$8$H$IfPkddE$$Ifl0>$644 la !"./049:@ABRSTU`aȾհհհՌ}o\}Ⱦհհ$jHhrhox#EHUnH o(tH j&_K hrhox#UVjhrhox#UnH tH hrh'nH tH hrhhnH tH hrhh6]nH tH hrhox#6]nH tH hrhox#]aJhrhox#_HEmH sH hrhox#nH tH hrhox#jhrhox#UjEhrhox#EHU$ʒ˒56DFGHiٓړߓ#$%5Lj~LjLjpjhrhox#5U\hrh-5\hrhox#5\hrhox#6H*]nH tH hrhox#6H*]nH tH hrhox#]aJhrhox#_HEmH sH  hrhox#hrh'nH tH hrhh6]nH tH hrhox#6]nH tH hrhox#nH tH (5PPkdJ$$Ifl0>$644 la x$7$8$H$IfPkdJ$$Ifl0>$644 la568ٓPPkdK$$Ifl0>$644 la x$7$8$H$IfPkdIK$$Ifl0>$644 laٓړ$ipՔ x$7$8$H$If$x$7$8$H$If U"#$ & FPkdK$$Ifl0>$644 la5678:;cdfghinpq”ÔȔǶǧǶǶucǜVL>hrhox#6]nH tH hrhox#]aJhrhox#_HEmH sH "j_Ohrhox#5EHU\o(/j}M hrhox#CJUVmH nHsH tHhrhox#mHnHsHtHhrhox#nH tH hrh'5\mHnHuhrhox#5\ hrhox#jhrhox#5U\"jTLhrhox#5EHU\o(/j=|M hrhox#CJUVmH nHsH tHȔ͔ΔՔ֔ה%'(456:?@GHI\ǽ܆|n`Qjhrhox#UnH tH hrh r6]nH tH hrhh6]nH tH hrhox#]aJhrhox#_HEmH sH "jQhrhox#5EHU\o(/j}M hrhox#CJUVmH nHsH tHhrhox#5\jhrhox#5U\ hrhox#hrhox#nH tH hrhox#6]nH tH hrh'nH tH Ք֔GH`?PkdOT$$Ifl0F$644 la x$7$8$H$If$x$7$8$H$Ifgd|UPkdQ$$Ifl0F$644 la\]^_ԕՕ ./notuvwĶįĶįĶįįįyi^jhrhox#Uhrhox#5\_HEmH sH hrhox#\hrh-5hrhox#5hrhox#6H*]nH tH hrhox#6H*]nH tH hrhox#hrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH !jThrhox#EHUnH tH jL hrhox#CJUV$PPkdV$$Ifl0F$644 la x$7$8$H$IfPkdV$$Ifl0F$644 la "nPPkdW$$Ifl0F$644 la x$7$8$H$IfPkdGW$$Ifl0F$644 lano˖Җ x$7$8$H$If$x$7$8$H$If U"#$ & FPkdW$$Ifl0F$644 laŖƖȖɖʖ˖ҖӖ_`bgiȺȖo^PEPhrh'nH tH hrhox#6]nH tH !j@[hrhox#EHUnH tH /j|M hrhox#CJUVmH nHsH tHjhrhox#UnH tH hrhox#nH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\ hrhox#jhrhox#UjRXhrhox#EHU/j}M hrhox#CJUVmH nHsH tHݗ=>и虏vdO=d#j`hrhox#6U]nH tH )j],J hrhox#6UV]nH tH #jhrhox#6U]nH tH hrh'nH tH hrhox#6]nH tH hrhox#]aJhrhox#_HEmH sH "j]hrhox#5EHU\o(/j}M hrhox#CJUVmH nHsH tHhrhox#5\jhrhox#5U\hrhox#nH tH hrhox#H*nH tH YJSkd>`$$IfF0F$ t644 la x$7$8$H$IfSkd]$$IfF0F$ t644 la>?DEFHILMNQRSZhjۘ jk™ƙՙњؚ ڼ诨wwi^jhrhox#Uhrhox#6aJmH sH hrhox#6]aJmH sH hrhox#aJmH sH hrhox#6aJhrhox#6] hrhox#hrhox#5\]aJhrhox#6H*]nH tH hrhox#6H*]nH tH hrhox#6]nH tH hrhox#nH tH hrhox#H*nH tH "YZ\ژJSkdb$$IfF0F$ t644 la x$7$8$H$IfSkdzb$$IfF0F$ t644 laژۘkɚPWoכ x$7$8$H$If U"# & F $7$8$H$Skd8c$$IfF0F$ t644 la  !"JKMNOPVWXklmnԛ֛כ؛ƸƓygXyNBhrhox#H*nH tH hrhox#6]j?@hijopqstwxy|}~學妔q_SSSShrhox#H*nH tH #j"khrhox#6U]nH tH )j],J hrhox#6UV]nH tH hrhox#6]nH tH #jhrhox#6U]nH tH hrhox#hrh'nH tH hrhox#6]!jhhrhox#EHUnH tH #j2L hrhox#CJPJUVhrhox#nH tH jhrhox#UnH tH ~ŜƜĝŝǝȝɝʝϝѝҝyoy`yThrhox#\nH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5j%nhrhox#EHUj,K hrhox#UVjhrhox#Uhrhox#aJmH sH hrhox#6H*]nH tH hrhox#6H*]nH tH hrhox#6]nH tH hrhox#hrhox#nH tH ZLkdam$$Ifl0F$64 la x$7$8$H$IfLkdl$$Ifl0F$64 laʝѝ()AHLkdr$$Ifl08$64 lax$If $7$8$H$ U"# & FLkdm$$Ifl0F$64 la!")*=>?@jkpuvĞɞʞԞ՞&4ԵԜԃxphrhox#H*jwhrhox#Ujr+J hrhox#UVjuhrhox#UjJ hrhox#UVjshrhox#UjJ hrhox#UV hrh'hrhox#6] hrhox#jhrhox#Ujphrhox#UjJ hrhox#UV(AӞԞ%_Lkdw$$Ifl08$64 laLkd$u$$Ifl08$64 lax$If%&(VWZ_LkdTz$$Ifl08$64 lax$IfLkdy$$Ifl08$64 la46Wfgßğן؟ٟڟ۟\g&'./23t̹̐sis퐀sVMhrhox#aJ$hrhox#_HEaJmH nHsH tHhrhox#]aJhrhox#aJmH sH hrhox#5\_HEmH sH hrhox#5\aJmH sH j{hrhox#UjJ hrhox#UVjhrhox#Uhrh|U5hrhox#5hrhox#6H*]nH tH hrhox#6] hrhox#hrhox#6H*]۟'3u&ݥn U" & F x X & F x# & F$Lkdz$$Ifl08$64 latu&./;ʤˤޤߤۥܥݥڰꨠuhڰS(jhrhox#0JH*UaJmH sH hrhsaJmH sH j}hrhox#UjJ hrhox#UV hrhox#jhrhox#Uhrh|U5hrhox#5hrhox#5\_HEmH sH hrhox#_HEmH sH hrhox#aJmH sH hrhox#5\aJmH sH hrhox#aJhrhox#_HEnHtHx¨'(IJKmnoͽͽ݋uf݃XNXhrhox#5\jhrhox#5U\j%hrhox#5EHUj K hrhox#UVhrhox#5jhrhox#5U(jhrhox#0JH*UaJmH sH hrhox#6]aJmH sH hrhox#5\_HEmH sH hrhox#5\aJmH sH  hrhox#hrhox#aJmH sH hrhox#H*aJmH sH ѩҩөԩ  3øÐshs\\Thrhox#H*hrhox#H*nH tH hrh'nH tH hrhox#6]nH tH jhrhox#UnH tH #jJ hrhox#UVnH tH jhrhox#UnH tH hrhox#hrhox#mH sH hrhox#nH tH hrhox#\nH tH hrhox#5jhrhox#5U\hrh'5\mHnHuթ7ELkdx$$Ifl0$f"64 laLkd$$Ifl0$f"64 la x$7$8$H$If$x$7$8$H$If#$ & F3456IJvw|ϪЪѪ34CDĶĶīĤĤĒĤtĤeĤYhrhox#5\aJhrhox#6H*]nH tH hrhox#6H*]nH tH j<hrhox#UnH tH #jFt+J hrhox#UVnH tH hrhox#hrh'nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH jxhrhox#UnH tH #jK hrhox#UVnH tH ϪЪ3ZLkd)$$Ifl0$f"64 laLkdچ$$Ifl0$f"64 la x$7$8$H$If34707OZUMF#$ & F U"# & FLkd$$Ifl0$f"64 la x$7$8$H$IfLkd$$Ifl0$f"64 la*+-./05678KLǺ䲤tiZtH#jK hrhox#UVnH tH jhrhox#UnH tH hrhox#mH sH hrhox#nH tH hrhox#\nH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5jOhrhox#EHU#ji-M hrhox#CJPJUVjhrhox#U hrhox#hrhox#aJhrhox#5\_HELMNuvw{ȬɬάӬԬ׬ج۬ݬެ߬Ⱥ֖֯֨֯{{saP!jޑhrhox#EHUnH tH #ji-M hrhox#CJPJUVhrhox#H*hrhox#H*nH tH juhrhox#UnH tH #jBJ hrhox#UVnH tH hrhox#hrh'nH tH hrhY\6]nH tH hrhox#6]nH tH hrhox#nH tH jhrhox#UnH tH j hrhox#UnH tH Oެ߬;ZI$x$7$8$H$IfgdpLkd|$$Ifl0$f"64 laLkd$$Ifl0$f"64 la x$7$8$H$If,.8:;?ȭɭʭݭޭ߭>?MOopȹzmbUhrhox#aJmH sH hrhox#5\]hrhox#5\]aJhrhox#6H*]nH tH hrhox#6H*]nH tH j6hrhox#UnH tH #j,J hrhox#UVnH tH jhrhox#UnH tH hrhox#hrhox#>*nH tH hrhox#H*nH tH hrhox#6]nH tH hrhox#nH tH ;ȭɭ>OLkd$$Ifl0$f"64 la x$7$8$H$IfLkdԓ$$Ifl0$f"64 la $7$8$H$If>?AopsZLkdؖ$$Ifl0$f"64 la x$7$8$H$IfLkdv$$Ifl0$f"64 laIrQ|IJ˲3 x$7$8$H$If $ $ U"# & F $7$8$H$Lkd:$$Ifl0$f"64 la HMTeRqrPQaձUVwx|}²IJ˲ŽصŽŒ}oeoVo}hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5jhrhox#EHUjޓIK hrhox#UVjhrhox#Uhrhox#H*\hrhox#]hrhox#\ hrhox#hrhox#6mH sH hrhox#mH sH hrhox#aJmH sH hrhox#6]aJmH sH  ˲̲߲$%02345HIJKuwx帪帪垓ra帪!jhrhox#EHUnH tH jIK hrhox#UV hrhox#hrhox#H*nH tH hrh'nH tH hrhox#nH o(tH hrhY\6]nH tH hrhox#6]nH tH !jOhrhox#EHUnH tH jIK hrhox#UVhrhox#nH tH jhrhox#UnH tH !34LdGkdɞ$$Ifl0O$64 la x$7$8$H$IfGkdR$$Ifl0O$64 la +-.:;>?@AOQqruĹħĊ|ĊpdXIXXhrhox#6H*]nH tH hrhox#nHo(tHhrhox#nH o(tH hrhox#H*nH tH hrhY\6]nH tH hrhox#6]nH tH jnhrhox#UnH tH #jJ hrhox#UVnH tH hrhox#nHtHhrhox#nH tH jhrhox#UnH tH j+hrhox#UnH tH #j J hrhox#UVnH tH  @ACqdGkdc$$Ifl0O$64 la x$7$8$H$IfGkd $$Ifl0O$64 laqrufd__WN $ $ U"# & FGkd'$$Ifl0O$64 la x$7$8$H$IfGkdţ$$Ifl0O$64 la "#:=ef޵1hmouؿ͸؛ؓ؛sa#jL hrhox#CJPJUVjhrhox#U]$jhrhox#0JH*UmH sH hrhox#H*hrhox#mH sH hrhox#]hrhox#57 hrh'jhrhox#Ujhrhox#U hrhox#hrhox#6H*\]hrhox#6\]hrhox#\ <=iklmnĵҭrdXQ hrhox#hrhox#H*nH tH hrhox#6]nH tH jhrhox#UnH tH #jK hrhox#UVnH tH hrhox#nH tH jhrhox#UnH tH hrhox#\hrh'5\mHnHujhrhox#5U\hrhox#5hrhox#5\jhrhox#U]jhrhox#EHU] lmLLkdA$$Ifl0X$64 laLkdީ$$Ifl0X$64 la x$7$8$H$If$x$7$8$H$If¶¨¶–¨¨¨¨{¨{p^#jJ hrhox#UVnH tH hrhox#nHtHhrhox#H*nH tH hrhox#6H*]nH tH hrhox#hrh'nH tH hrhox#6]nH tH hrhox#nH o(tH hrhox#nH tH jhrhox#UnH tH !j@hrhox#EHUnH tH #jcL hrhox#CJPJUV bceILkd$$Ifl0X$64 la x$7$8$H$If$x$7$8$H$IfgdnHLkd$$Ifl0X$64 laKMZ\bcqsƶƶƧtetSGS:hrhox#aJmH sH hrhox#5\aJ"hrhox#5\mH nH sH tH hrhox#6H*]nH tH hrhox#nHtHhrhox#nH tH hrhox#6H*]nH tH hrhox#6]nH tH hrhox#mH nHsH tHhrhox#H*mH nH sH tH hrhox#mH nH sH tH hrhox#nH o(tH jhrhox#UnH tH jhrhox#UnH tH >VZSNNG#$ & F# & F# & FLkd$$Ifl0X$64 la x$7$8$H$IfLkdG$$Ifl0X$64 la#Ĺ;=>UV\]^BCDEľ˾оؾI㻭ܠܙܒܒ܄ynZMnj hrhox#EHU'jJRM hrhox#CJUVnHtHjhrhox#Uhrhox#mH sH hrhox#6]mH sH  hrhylh hrhrjhrhox#H*Uhrhox#5\mH sH "hrhox#5\mH nH sH tH hrhox#mH nH sH tH hrhox#hrhox#aJmH sH hrhox#6]aJmH sH V_Ix$If #$ & F # U"$gd\$ & F 85O^5`OgdnH$ & F 85O^5`O$ & F 85]^5`]gdr$ IJ]^_`abcϾ尢~waT~J?whrhox#nHtHhrhox#6H*jIhrhox#EHU+jWVM hrhox#CJPJUVnHtH hrhox#jhrhox#Uhrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5\mH sH !jDhrhox#EHUmH sH +jk^VM hrhox#CJPJUVnHtHhrhox#mH sH jhrhox#UmH sH   S`abcvwxyzǿvoYLvDhrhox#]jFhrhox#EHU+j+XVM hrhox#CJPJUVnHtH hrhox#jhrhox#Uhrhox#B*]phhrhox#B*phhrhox#6B*H*phhrhox#6B*phhrhox#mH sH hrhox#H*hrhox#H*nHtHhrhOnHtHhrhox#6]nHtHhrhox#nHtHhrhox#6abzOB $x$IfgdnHSkd$$Ifl0X$ t644 lax$IfSkd$$Ifl0X$ t644 la5678=>?VWjklmnxz}ȽҤvjjȽ\hrhox#6]mH sH hrhox#H*mH sH j hrhox#EHU3j^VM hrhox#CJPJUVmH nHsH tH hrhox#jhrhox#Uhrhox#6]nHtHhrhox#6H*]hrhox#6]hrhox#mH sH hrhox#B*phhrhox#nHtHhrhox#H*nHtH ?@7OF=#$ & F # & F #Skd$$Ifl0X$ t644 lax$IfSkdL$$Ifl0X$ t644 la7yz}~￲煮thYjhrhox#UnH tH hrhox#H*nH tH jhrhox#Uj "I hrhox#UVhrh'5\mHnHujhrhox#5U\hrhox#5jhrhox#EHU3j YM hrhox#CJPJUVmH nHsH tHjhrhox#Uhrhox#nH tH hrhox#hrhox#5\7}~Lkd$$Ifl0X$64 la x$7$8$H$If $x$If#$ & F U"# & F #$%dh,-01ĸĪĸĪćugu`uVVVhrhox#6] hrh'jhrhox#Ujhrhox#U hrhox#hrhox#>*hrhox#H*nH tH hrhox#6H*]nH tH hrhox#6]nH tH hrhox#H*nH tH hrhox#nH tH jhrhox#UnH tH jhrhox#UnH tH #jJ hrhox#UVnH tH cd }ZUUMU# & FgdY # & FLkd}$$Ifl0X$64 la x$7$8$H$IfLkd$$Ifl0X$64 la124567 <=5}~ôШШПxi[Q[hrhox#5\jhrhox#5U\j\hrhox#EHPJU3jȦM hrhox#CJPJUVmH nHsH tHjhrhox#PJUhrhox#PJhrhox#H*nH tH hrhox#5H*\]aJhrhox#5\]aJhrhox#nH tH hrhox#H*hrhox#6] hrhox#hrhox#6H*]AEFHIJKǥΆucuQ=Qudž&hrhox#CJH*OJPJQJ]^J#hrhox#CJOJPJQJ]^J#hrhox#CJH*OJPJQJ^J hrhox#CJOJPJQJ^J#hrhox#6CJOJPJQJ^Jjzhrhox#EHUCj妈M hrhox#CJOJPJQJUV^JaJmH nHsH tH hrhox#jhrhox#Uhrhox#PJjhrhox#5U\hrh'5\mHnHu}IJM\AXkd$$Ifl0T$ t644q4la, $ x$%d&d'd9DIfOPQ[$\$(x$%d&d'd9DIfOPQ[$\$#$ & F # & F (#KLY[\]^qrst5ACDvwx·•tbbbtO%jhrhox#CJOJQJU^J#hrhox#6CJOJPJQJ^J&hrhox#CJH*OJPJQJ]^Jjihrhox#EHUCjM hrhox#CJOJPJQJUV^JaJmH nHsH tHjhrhox#U hrhox##hrhox#CJOJPJQJ]^J hrhox#CJOJPJQJ^J&hrhox#6CJH*OJPJQJ^J\]u~~&Xkd$$Ifl0T$ t644q4la(x$%d&d'd9DIfOPQ[$\$Xkd$$Ifl0T$ t644q4lavOXkd$$Ifl0T$ t644q4la. x$%d&d'd9DIfOPQ[$\$*$x$%d&d'd9DIfOPQ[$\$vw~Q, px$%d&d'd9DIfOPQ[$\$(x$%d&d'd9DIfOPQ[$\$XkdQ$$Ifl0T$ t644q4lax Ӿvb[I5I&hrhox#6CJH*OJPJQJ^J#hrhox#6CJOJPJQJ^J hrhox#&hrhox#CJH*OJPJQJ]^J#hrhox#CJOJPJQJ]^J#hrhox#CJH*OJPJQJ^J hrhox#CJOJPJQJ^J%jhrhox#CJOJQJU^J)jhrhox#CJEHOJQJU^J;jJ hrhox#CJOJPJQJUV^JaJnH tH hrhox#CJOJQJ^J)}P,  x$%d&d'd9DIfOPQ[$\$*$x$%d&d'd9DIfOPQ[$\$Xkd$$Ifl0T$ t644q4la &()*-01PQȴȎڇsaȴȴȎڇSIhrhox#5\hrhox#5\nH tH #hrhox#CJH*OJPJQJ^J&hrhox#6CJH*OJPJQJ^J hrhox#&hrhox#CJH*OJPJQJ]^J#hrhox#6CJOJPJQJ^J&hrhox#CJH*OJPJQJ]^J#hrhox#CJOJPJQJ]^J hrhox#CJOJPJQJ^J(jhrhox#0JCJH*PJU^J)*1~Q,  x$%d&d'd9DIfOPQ[$\$(x$%d&d'd9DIfOPQ[$\$Xkd.$$Ifl0T$ t644q4la"I{m` x$7$8$H$If$x$7$8$H$If#$ & F U"# & F$#$ & F ^`Xkd$$Ifl0T$ t644q4la"HIJ]^_`abc#ƹ㱣{iZ{Nhrhox#H*nH tH jhrhox#UnH tH #j"I hrhox#UVnH tH jhrhox#UnH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5jhrhox#EHU#j('M hrhox#UVmH sH jhrhox#U hrhox#hrhox#nH tH hrhox#mH sH 9yy x$7$8$H$If#$ & F U"# & F#$ & F ^`gdY Okd$$Ifl40K$64 laf4#$*4589:MNOPQRS{|~丫䣕|paO#jw"I hrhox#UVnH tH jhrhox#UnH tH hrhox#\nH tH hrh'5\mHnHuhrhox#5\jhrhox#5U\hrhox#5jShrhox#EHUj1J hrhox#UVjhrhox#Uhrhox#nH tH hrhox#H* hrhox#hrhox#6H*]hrhox#6]'(+,-@ABCwx{|}ֱ֔qbj@hrhox#UnH tH #j"I hrhox#UVnH tH !jhrhox#EHUnH tH jBK hrhox#UVjPhrhox#UnH tH #jJ hrhox#UVnH tH hrhox#hrhox#H*nH tH hrhox#nH tH jhrhox#UnH tH jhrhox#UnH tH !+,D{TOkdh$$Ifl40<$z64 laf4 x$7$8$H$IfOkd$$Ifl40<$z64 laf4{|'RHH@ U" #$ & FgdnHQkd.$$Ifl40<$z64 laf4 x$7$8$H$IfOkd$$Ifl40<$z64 laf4RSVWXZ[\·¬¬¬ӝӒqd\hrhox#5jhrhox#EHU+j["I hrhox#UVmH nH sH tH jhrhox#Uhrhox#nH tH jhrhox#0JH*Uhrhox#6H*]hrhox#6H*]hrhox#6] hrh' hrhox#hrhox#5]nHtHhrhox#]aJhrhox#5\]aJ!"$%&'(;<=>?@AijlmnotuvwĹĄvk]j"I hrhox#UVjhrhox#Ujp"I hrhox#UVhrhox#nH tH j hrhox#EHU+jI hrhox#UVmH nH sH tH hrhox#jhrhox#Uhrhox#\nH tH hrhox#5hrh'5\mHnHuhrhox#5\jhrhox#5U\!'ovOkd$$Ifl40!$l64 laf4x$If $x$If#$ & F U"2345{|}Fst⿴⿬➓⿴⿬⋂uj`hrhox#5aJhrhox#nHtHhrhox#_HEnHtHhrhox#aJhrhox#5jhrhox#Uj"I hrhox#UVhrhox#H*hrhox#6H*]hrhox#6]j_hrhox#Ujz"I hrhox#UV hrhox#jhrhox#Ujhrhox#U%6YOkd$$Ifl40!$l64 laf4x$IfOkd$$Ifl40!$l64 laf4Ft~Q$$If Q$Ifgd\# & F#$ & F#$ & F ^`Okd$$Ifl40!$l64 laf4 %&67;<=deŸШŕŨŨ{ŨŨhŨ\иhrhox#6]aJ$jhrhox#B*Uph$jfhrhox#B*Uph hrh'$jhrhox#B*Uphjhrhox#B*Uphhrhox#aJnHtHhrhox#B*phhrhox#aJhrhox#5aJhrhox#6H*\]aJhrhox#6\]aJ$xogQ$$If Q$Ifgd\kdw$$IfF0$FB  0644 lap =xppQ$$Ifkd0$$IfF0$FB  0644 lap =>KfxppQ$$Ifkd`$$IfF0$FB  0644 lap fgwvnnQ$$Ifkd$$IfF-0$FB  0644 lap xppQ$$Ifkd$$IfF0$FB  0644 lap xppQ$$Ifkd$$IfF0$FB  0644 lap xtkcQ$$If Q$IfgdY JkdH$$IfF0$FB  0644 lap 12HIYZ]^_m Ůꤛَvoٛ[J hrhox#aJmH nHsH tH&hrhox#6OJQJ]^JnH tH hrh'/jnhrhox#OJQJU^JnH tH hrhox#aJnHtHhrhox#aJhrhox#5aJ-jhrhox#EHOJQJU^JnH tH 'jxJ hrhox#CJUVmH sH  hrhox#OJQJ^JnH tH )jhrhox#OJQJU^JnH tH xogQ$$If Q$IfgdY kd$$IfF0$>J  0644 lap 1_xogQ$$If Q$IfgdY kd$$IfF0$>J  0644 lap _`m xogQ$$If Q$IfgdY kd$$IfF0$>J  0644 lap  O`xogggggQ$$If Q$IfgdY kd$$IfF0$>J  0644 lap HM )*+,>?RS︯{fUA'jJ hrhox#CJUVmH sH  hrhox#OJQJ^JnH tH )jhrhox#OJQJU^JnH tH hrhox#5aJhrhox#aJmH sH hrhox#_HEmH sH hrhox#6]_HEmH sH hrhox#aJhrhox#aJnHtH"hrhox#6\_HEaJnHtH/jhrhox#0JH*U\_HEaJnHtHhrhox#\_HEaJnHtH9:xrjQ$$IfQ$Ifkd]$$IfF0$>J  0644 lap :;H*xrg Q$$IfgdQ$Ifkd$$IfF0$>J  0644 lap *+,>WxtllQ$$IfJkd$$IfF0$>J  0644 lap STUVXdqrXYZk ;¸¢ŠӃkӃ¯W&hrhox#6OJQJ]^JnH tH /jhrhox#OJQJU^JnH tH hrh'/jhrhox#OJQJU^JnH tH hrhox#aJnHtHhrhox#aJhrhox#5aJ hrhox#OJQJ^JnH tH )jhrhox#OJQJU^JnH tH -jhrhox#EHOJQJU^JnH tH WXdrxppQ$$Ifkd$$IfF0$"3  0644 lap rsxppQ$$IfkdL$$IfF0$"3  0644 lap ZxmeQ$$If Q$$Ifgd\kd$$IfF0$"3  0644 lap Z[kJ xrjjjjjQ$$IfQ$Ifkd$$IfF0$"3  0644 lap  ,-xrrQ$Ifkdq$$IfF0$"3  0644 lap -.;xpe Q$$IfgdQ$$Ifkd*$$IfF0$"3  0644 lap ;?,-@ABCEPUW\]qrózsksZFZ'j hrhox#UaJnHtH!jhrhox#UaJnHtHhrhox#H* hrhox#"jhrhox#B*EHUph7jKM hrhox#CJPJUVaJmH nHsH tHhrhox#B*phjhrhox#B*Uphhrhox#5aJhrhox#aJnHtHhrhox#aJhrhox#_HEmH sH hrhox#6]_HEmH sH ,DxtkcQ$$If Q$IfgdHCJkd$$IfF0$"3  0644 lap DEP]xogQ$$If Q$IfgdHCkd| $$IfF0$3U  0y644 lap ]^qxogQ$$If Q$IfgdHCkd5 $$IfF0$3U  0y644 lap 0CHJ]^۾۾ۚkY۾"jhrhox#B*EHUph'j6K hrhox#UVaJmH sH hrhox#B*phjhrhox#B*Uphhrhox#5aJhrhox#H*hrhox#mH sH  hrhox#hrhox#aJ'jk hrhox#UaJnHtHhrhox#aJnHtH!jhrhox#UaJnHtH hrh'"xogQ$$If Q$IfgdHCkd $$IfF0$3U  0y644 lap  0^xogQ$$If Q$IfgdHCkd $$IfF0$3U  0y644 lap ^_xrjQ$$IfQ$IfkdZ $$IfF0$3U  0y644 lap xppQ$$Ifkd$$IfF0$3U  0y644 lap xtkcQ$$If Q$IfgdHCJkd$$IfF0$3U  0y644 lap xogQ$$If Q$IfgdHCkdf$$IfF0$/Y  0644 lap xogQ$$If Q$IfgdHCkd$$IfF0$/Y  0644 lap &-QRcuz|ὶὠ{pbM{)jhrhox#EHUmH nH sH tH jJ hrhox#UVhrhox#nH tH %jhrhox#UmH nH sH tH hrhox#5aJhrhox#H*hrhox#mH sH hrhox#nHtH hrhox#hrhox#aJ hrh''jhrhox#UaJnHtHhrhox#aJnHtH!jhrhox#UaJnHtH&RxppQ$$IfkdU$$IfF0$/Y  0644 lap RScxppQ$$Ifkd$$IfF0$/Y  0644 lap xrjQ$$IfQ$Ifkd$$IfF0$/Y  0644 lap xppQ$$Ifkd$$IfF0$/Y  0644 lap xtn` $$7$8$H$Ifa$Q$IfJkd9$$IfF0$/Y  0644 lap 23CDGHJKabrsvwyzԻߪ{g'jNhrhox#UaJnHtH'jhrhox#UaJnHtH hrh''jThrhox#UaJnHtH!jhrhox#UaJnHtHhrhox#aJnHtHhrhox#H*nH tH hrhox#nH tH hrhox#aJhrhox#5aJhrhox#6]nH tH "xppQ$$Ifkd$$IfF0$;M  0644 lap xppQ$$Ifkd$$IfF0$;M  0644 lap HIJ[)޲ͧޞާvjޞ`hrhox#5aJhrhox#H*nH tH hrhox#mH sH hrhox#mH nH sH tH hrhox#6]nH tH hrhox#aJhrhox#nH tH 'jHhrhox#UaJnHtH hrh'!jhrhox#UaJnHtHhrhox#aJnHtH'jhrhox#UaJnHtH JxppQ$$Ifkd$$IfF0$;M  0644 lap JK[[xppppppQ$$Ifkd~$$IfF0$;M  0644 lap xppQ$$Ifkd7$$IfF0$;M  0644 lap xppQ$$Ifkd$$IfF0$;M  0644 lap )Bxtk` Q$$Ifgdylh Q$IfgdylhJkd$$IfF0$;M  0644 lap )*=>?@ACNSUZ[op𳩠ujXjuMujBhrhox#nHtHhrh'mH sH #j#hrhox#UmH sH hrhox#mH sH jhrhox#UmH sH hrhox#aJnHtHhrhox#H* hrhox#hrhox#aJhrhox#5aJhrhox#H*nHo(tH"jb hrhox#B*EHUph#jJ hrhox#UVmH sH hrhox#B*phjhrhox#B*UphBCN[xmm Q$$IfgdylhkdB"$$IfF0$"A  0644 lap [\oxmm Q$$Ifgdylhkd"$$IfF0$"A  0644 lap xmm Q$$Ifgdylhkd1$$$IfF0$"A  0644 lap xmm Q$$Ifgdylhkd$$$IfF0$"A  0644 lap 9:LM`abcepxz{Ʒ}kdR#j+hrhox#UnH tH hrh'#j/+hrhox#UnH tH hrhox#H*nH tH !j'hrhox#EHUnH tH #jJ hrhox#UVmH sH hrhox#nH tH jhrhox#UnH tH hrhox#5aJhrhox#aJnHtHhrhox#H* hrhox#hrhox#mH sH hrhox#aJ ()xod Q$$Ifgdylh Q$Ifgdylhkd%$$IfF0$"A  0644 lap )*78xmm Q$$Ifgdylhkd\&$$IfF0$"A  0644 lap 89:LdxtkcQ$$If Q$IfgdHCJkd'$$IfF0$"A  0644 lap dep{xogQ$$If Q$IfgdHCkd)$$IfF0%"O  0q%644 lap {|#xogQ$$If Q$IfgdHCkdv*$$IfF0%"O  0q%644 lap !"#1PQRcޭޟynV/jo-M hrhox#CJPJUVaJmH sH hrhox#mH sH jhrhox#UmH sH hrhox#5\hrhox#aJnHtHhrhox#6]nH tH hrhox#aJhrh,nH tH hrhnH tH #j),hrhox#UnH tH hrhox#nH tH hrh'jhrhox#UnH tH #$1RxogQ$$If Q$IfgdHCkd,$$IfF0%"O  0q%644 lap RSccxrrrrjQ$$IfQ$Ifkd_-$$IfF0%"O  0q%644 lap xppQ$$Ifkd.$$IfF0%"O  0q%644 lap xppQ$$Ifkd.$$IfF0%"O  0q%644 lap xtkb Q$$$If Q$IfgdHCJkd/$$IfF0%"O  0q%644 lap )13GHI_`pquvwxNPqƻ߻ߍ߻ƻƀƦƦvj\jhrhox#6H*mHsHhrhox#6mHsHhrhox#5\hrhox#aJnHtH hrh'#j3hrhox#UmH sH hrhox#aJhrhox#H*mH sH hrhox#mH sH  hrhox#hrhox#5aJhrhox#5jhrhox#UmH sH !jC0hrhox#EHUmH sH !)4uldQ$$If Q$IfgdHCkd92$$IfF40$;M  0644 laf4p 45HwummQ$$Ifkd2$$IfF40$;M  0644 laf4p wxummQ$$Ifkd44$$IfF40$;M  0644 laf4p +OumgggmQ$IfQ$$Ifkd4$$IfF40$;M  0644 laf4p OPquogQ$$IfQ$Ifkd5$$IfF40$;M  0644 laf4p ummQ$$Ifkdq6$$IfF40$;M  0644 laf4p uqkcQ$$IfQ$IfJkd07$$IfF40$;M  0644 laf4p ./3467MN^_cdef5¹ܪtjjjܹ[hrhox#_HEaJnHtHhrhox#6]#j9hrhox#UmH sH  hrh'#jm9hrhox#UmH sH hrhox#mH sH jhrhox#UmH sH hrhox#aJhrhox#H*#hrhox#H*_HEmH nHsH tH hrhox#hrhox#5aJhrhox#5hrhox#mHsH#uogQ$$IfQ$Ifkd7$$IfF40$:N  0644 laf4p eummQ$$Ifkd8$$IfF40$:N  0644 laf4p efsummQ$$Ifkdg:$$IfF40$:N  0644 laf4p ummQ$$Ifkd&;$$IfF40$:N  0644 laf4p 5r$%&'9:MNOϼϭϭϠƄzoUHj">hrhox#EHU3j좀M hrhox#CJPJUVmH nHsH tHjhrhox#Uhrhox#5\hrhox#aJnHtHhrhox#PJ_HEnHtHhrhox#_HEnHtHjhrhox#0JH*Uhrhox#6]hrhox#aJ hrhox#hrhox#6_HEaJnHtHhrhox#_HEaJnHtHhrhox#PJaJummQ$$Ifkd;$$IfF40$:N  0644 laf4p |uumaW8 & F  [<$7$8$H$If^`[gdHC # & F$If # & F$IfQ$$Ifkd<$$IfF40$:N  0644 laf4p u%&-kdc=$$IfF40$:N  0644 laf4p Q$<$If & F  [<$7$8$H$If^`[gdHC & F  w<$7$8$H$If^`wgdHC&'9jkvckdMC$$IfF40$;M  0644 laf4p Q$$IfQ$IfJOPRSfghijkvt^t^QHhrhox#aJhrhox#aJmH sH +hrhox#H*OJQJ^JmH nH sH tH (hrhox#OJQJ^JmH nH sH tH hrhox#H*mH sH #hrhox#H*_HEmH nHsH tHhrhox#mH sH hrhox#5aJhrhox#5j@hrhox#EHU7j.M hrhox#CJPJUVaJmH nHsH tH hrhox#jhrhox#U ummQ$$Ifkd D$$IfF40$;M  0644 laf4p  89N~ ߿꟏si\ihrhox#5\]aJhrhox#]aJhrhox#]aJmH sH hrhox#_HEmH o(sH hrhox#6]_HEmH sH hrhox#_HEmH sH hrhox#6]hrhox#aJhrhox#mH sH jHEhrhox#U hrh'jhrhox#U hrhox#jDhrhox#U! RummQ$$IfkdE$$IfF40$;M  0644 laf4p  !-.79EFJOQRSciúëúúëÑÄuúh^hrhox#5aJhrhox#aJnHtHhrhox#PJ_HEnHtHhrhox#_HEnHtHjhrhox#0JH*Uhrhox#PJaJhrhox#_HEaJnHtHhrhox#aJ hrhox# hrh'OJQJ^JnH tH hrhox#OJQJ^JnH tH &hrhox#6OJQJ]^JnH tH RScummQ$$IfkdF$$IfF40$;M  0644 laf4p ummQ$$IfkdCG$$IfF40$;M  0644 laf4p iiumaW; & F  D<$7$8$H$If^`D # & F$If # & F$IfQ$$IfkdH$$IfF40$;M  0644 laf4p ii3/JkdH$$IfF40$;M  0644 laf4p Q$<$If & F  ]<$7$8$H$If^`] & F  k<$7$8$H$If^`k(pkdK$$IfF0$>J  0644 lap Q$$If    "%'(<=STdehijxBvϾ埒ykkk_hrhox#>*nH tH hrhox#6]nH tH hrh'#jLhrhox#UnH tH hrhox#aJnHtHhrhox#H*nH tH hrhox#aJhrhox#5aJ!jIhrhox#EHUnH tH +j_K hrhox#PJUVaJmH sH hrhox#nH tH jhrhox#UnH tH %()<jxppQ$$IfkdDL$$IfF0$>J  0644 lap jkxxppQ$$IfkdzM$$IfF0$>J  0644 lap BxppQ$$Ifkd3N$$IfF0$>J  0644 lap BCdhxppQ$$IfkdN$$IfF0$>J  0644 lap hivXxrj`` Q$x$IfQ$$IfQ$IfkdO$$IfF0$>J  0644 lap -./0YZlmϾ婜|k_Q@_ jhrhox#U]nH tH hrhox#H*]nH tH hrhox#]nH tH !j"Shrhox#EHUnH tH +j_K hrhox#PJUVaJmH sH hrhox#5aJhrhox#aJnHtHhrhox#aJhrhox#>*nH tH !j^Phrhox#EHUnH tH +j_K hrhox#PJUVaJmH sH hrhox#nH tH jhrhox#UnH tH XYZlxtkcQ$$If Q$IfgdHCJkdiR$$IfF0$>J  0644 lap xogQ$$If Q$IfgdHCkd)U$$IfF0$FB  0644 lap xppQ$$IfkdU$$IfF0$FB  0644 lap #$)./0   "-6࿴uaPuGhrhox#PJ!jZhrhox#EHUnH tH 'jK hrhox#UVaJmH sH jhrhox#UnH tH hrhox#5aJhrhox#aJnHtHhrh'nH tH hrhox#6]nH tH hrhox#nH tH hrhox#aJ hrh' jhrhox#U]nH tH hrhox#]nH tH &jVhrhox#U]nH tH 1xppQ$$IfkdW$$IfF0$FB  0644 lap 12BcxppQ$$IfkdW$$IfF0$FB  0644 lap cdxppQ$$IfkdX$$IfF0$FB  0644 lap xppQ$$IfkdCY$$IfF0$FB  0644 lap  !xtllQ$$IfJkdY$$IfF0$FB  0644 lap !"-JxppQ$$Ifkd\$$IfF0$03  0644 lap 68CEGIJ^_uv=ǼǣǼǼǣǼǼǣǼtitb hrhox#hrhnH tH hrhsnH tH #j_hrhox#UnH tH #j^hrhox#UnH tH hrh'#j^hrhox#UnH tH hrhox#nH tH jhrhox#UnH tH hrhox#aJhrhox#aJnHtHhrhox#PJhrhox#H*PJ%JK^xppQ$$IfkdM]$$IfF0$03  0644 lap ?xppQ$$Ifkd}_$$IfF0$03  0644 lap =>?P   8 : ; < = A C D V W j k l m o z           ػβꨙraᙎ!jchrhox#EHUnH tH 7j!M hrhox#CJPJUVaJmH nHsH tHhrhox#nH tH jhrhox#UnH tH hrhox#5aJhrhHCPJhrhHCH*PJhrhOPJhrhox#H*PJhrhox#PJhrhox#aJhrhox#aJnHtHhrhox#6"?@PyxrrrrrQ$Ifkd6`$$IfF0$03  0644 lap xppQ$$Ifkd`$$IfF0$03  0644 lap B xrg Q$$IfgdOQ$Ifkda$$IfF0$03  0644 lap B C D V n xtllQ$$IfJkdab$$IfF0$03  0644 lap n o z  xppQ$$Ifkde$$IfF0$"A  0644 lap     xppQ$$Ifkde$$IfF0$"A  0644 lap         & ' ( 9   z   @K#$%&(3⵨è␆è~hW~P hrhox#!jjhrhox#EHUnH tH +j_K hrhox#PJUVaJmH sH hrhox#5hrhox#6PJhrhox#PJhrhox#_HEaJnHtHhrhox#aJnHtHhrhox#6]nH tH hrhox#aJ hrh'jhrhox#UnH tH hrhox#nH tH #jfhrhox#UnH tH    ( xppQ$$Ifkd g$$IfF0$"A  0644 lap ( ) 9 n  b  xpdddd Q$ e@$IfQ$$Ifkdg$$IfF0$"A  0644 lap     xrjQ$$IfQ$Ifkd{h$$IfF0$"A  0644 lap      xrjWL Q$ & F$IfQ$ & F he$IfgdM\Q$$IfQ$Ifkd4i$$IfF0$"A  0644 lap 'xtllQ$$IfJkdi$$IfF0$"A  0644 lap '(3;rjjQ$$Ifkdl$$IfF40$FB  t 0644 laf4p 3458:<NOPfgwx{|}q;?Cĩޞxޞl՞xdhrhox#5hrhox#>*nH tH hrhox#aJnHtHhrh'nH tH hrhox#6]nH tH hrhox#nH tH hrh'&j$nhrhox#U]nH tH jhrhox#U]nH tH hrhox#aJ hrhox#hrhox#H*]nH tH hrhox#]nH tH ";<O}rjjQ$$Ifkdmm$$IfF40$FB  t 0644 laf4p }~rjjQ$$Ifkdn$$IfF40$FB  t 0644 laf4p rrjjQ$$IfkdXo$$IfF40$FB  t 0644 laf4p rsrjjQ$$Ifkdp$$IfF40$FB  t 0644 laf4p ;rjjjQ$$Ifkdp$$IfF40$FB  t 0644 laf4p rnffQ$$IfJkd}q$$IfF40$FB  t 0644 laf4p *+/01?}폃odYNjhrh Uhrh mH sH hrh'mH sH &juhrhox#U]nH tH hrhox#]nH tH jhrhox#U]nH tH hrhox#aJhrhox#H*nHtHhrhox#nHtHhrhox#5j4rhrhox#EHU/j+XVM hrhox#CJPJUVaJnHtH hrhox#jhrhox#UrjjQ$$Ifkd4t$$IfF40$FB  t 0644 laf4p 1rj^ Q$$If]Q$$Ifkdt$$IfF40$FB  t 0644 laf4p 12?~rjjQ$$Ifkdv$$IfF40$FB  t 0644 laf4p ~rjjQ$$Ifkdv$$IfF40$FB  t 0644 laf4p &'24?DFXYZptkZNhrhox#]nH tH jhrhox#U]nH tH hrhox#aJhrhox#nHtHhrhox#6H*]hrhox#6]hrhox#5hrhox#aJnHtH hrhox#hrh H*mH sH hrh mH sH jhrh Ujwhrh EHU3j^VM hrh CJPJUVmH nHsH tH hrh rjjQ$$Ifkdy$$IfF40$FB  t 0644 laf4p rjjQ$$IfkdJz$$IfF40$FB  t 0644 laf4p &3rnffQ$$IfJkd{$$IfF40$FB  t 0644 laf4p 34?ErjjQ$$Ifkd{$$IfF40$>J  t 0644 laf4p EFYrjjQ$$Ifkdo|$$IfF40$>J  t 0644 laf4p pq   0g #Hི}p_pVL_hrhox#5\hrhox#aJ hrhox#_HEmH nHsH tHhrhox#aJnHtHhrhox#CJ\hrh 6H*]hrh 6]hrhQUmH sH hrh mH sH hrhox#nHtH hrhox#hrh'mH sH  jhrhox#U]nH tH hrhox#]nH tH &j&}hrhox#U]nH tH rjjQ$$Ifkd}$$IfF40$>J  t 0644 laf4p 1rjjQ$$IfkdZ~$$IfF40$>J  t 0644 laf4p 12SWrjjQ$$Ifkd$$IfF40$>J  t 0644 laf4p WXefrjjQ$$Ifkd$$IfF40$>J  t 0644 laf4p fg#HridOd@ & F7$8$H$gdylh# & F @ ^`gdM\# & FK gdY kd$$IfF40$>J  t 0644 laf4p MNOW^  ?!!!!!!ǹǹǹǹǧ~nhrhox#mH nHo(sH tHhrhox#\mH sH hrhox#\]mH sH hrhox#mH nHsH tH#hrhox#56>*\]nH tH hrhox#6]nH tH hrhox#nH tH hrhox#5\hrhox#6]_HEnHtH hrhox#hrhox#_HEnHtH(NZ   ;"Y"$# & FxM & F#x & F#xgdylhM$gdY # & F# & F @ ^`gdM\ & F & F p$ & F7$8$H$gdY & F p!""" ";"Y"""$$$$$ % %!%"%2%3%7%8%:%;%Q%R%b%c%g%h%j%k%%ºzjzczzSzczzj1hrhox#UaJ hrh'jhrhox#UaJjhrhox#UaJhrhox#aJhrhox#6H*]hrhox#6]hrhox#5aJhrhox#6\]hrhox#\hrhox#5#hrhox#_HEmH nHo(sH tH$hrhox#PJ_HEmH nHsH tH hrhox#_HEmH nHsH tH $$$$$$gkd6$$IfF40$4T  0644 laf4p Q$$IfQ$If$$ %%ummQ$$Ifkd$$IfF40$4T  0644 laf4p %%%%%%%%%%%%%%%%%%&9':'L'M'Q'S'^'_'`'t'u'v''ٷ欞欉wmf\fhrhox#H*aJ hrhox#hrhox#5aJhrhox#6H*hrhox#6hrhox#5\hrhox#nH tH hrhox#6]mH sH hrhox#mH sH hrh'mH sH j+hrhox#UaJ hrh'jhrhox#UaJhrhox#aJjhrhox#UaJ%%%%ummQ$$Ifkd$$IfF40$4T  0644 laf4p %%%&ummQ$$Ifkdg$$IfF40$4T  0644 laf4p &&&&uma Q$h$If^hQ$$Ifkd&$$IfF40$4T  0644 laf4p &&''ummQ$$Ifkd$$IfF40$4T  0644 laf4p ''(')'ummQ$$Ifkd$$IfF40$4T  0644 laf4p )'*'7'8'ummQ$$Ifkdc$$IfF40$4T  0644 laf4p 8'9':'L'R'uqiiQ$$IfJkd"$$IfF40$4T  0644 laf4p R'S'^'a'ummQ$$Ifkd$$IfF40$4T  0644 laf4p a'b'u''ummQ$$Ifkd$$IfF40$4T  0644 laf4p ''''''''''''( (((((((((!)")#)5)6)I)J)K)L)N)Y)o)p)q))˺毥wf\hrhox#5aJ!jhrhox#EHUnH tH 'jL hrhox#CJPJUVaJhrhox#nH tH jhrhox#UnH tH hrhox#5\hrhox#mH sH  hrh$hrhox#6] hrhox# hrh'jhrhox#UaJhrhox#aJj_hrhox#UaJ$''''ummQ$$Ifkd܋$$IfF40$4T  0644 laf4p '''(ummQ$$Ifkd$$IfF40$4T  0644 laf4p ((?((ummQ$$IfkdZ$$IfF40$4T  0644 laf4p ((((ummQ$$Ifkd$$IfF40$4T  0644 laf4p ((((ummQ$$Ifkd؎$$IfF40$4T  0644 laf4p (((!)ummQ$$Ifkd$$IfF40$4T  0644 laf4p !)")#)5)M)soggQ$$IfJkdV$$IfF40$4T  0644 laf4p M)N)Y)\)ummQ$$Ifkd$$IfF40$4T  0644 laf4p \)])p))ummQ$$Ifkd$$IfF40$4T  0644 laf4p )))))))))))))))** **-*O*P*g*h*{*|**********滱榜kY"jhrhox#B*EHUph+j7~MK hrhox#PJUVaJmH sH hrhox#B*phjhrhox#B*Uphhrhox#5aJhrhox#mH sH hrhox#6] hrhox#jhrhox#UaJ hrh'jhrhox#UaJhrhox#aJj~hrhox#UaJ"))) *ummQ$$Ifkdx$$IfF40$4T  0644 laf4p  * **,*ummQ$$Ifkd7$$IfF40$4T  0644 laf4p ,*-*N*O*ummQ$$Ifkd$$IfF40$4T  0644 laf4p O*P*f*g*ummQ$$Ifkd$$IfF40$4T  0644 laf4p g*h*z*{*ummQ$$Ifkdt$$IfF40$4T  0644 laf4p {*|***ummQ$$Ifkd3$$IfF40$4T  0644 laf4p *****uqkcQ$$IfQ$IfJkd$$IfF40$4T  0644 laf4p *********++++++@+D+N+P+++++++,$,%,&, -F-G-Y-Z-m-ٸʱ䤖|rkdd|rkd hrhox# hrh"1hrhox#5\hrhox#5]hrhox#6]aJmH sH hrhox#6aJmH sH hrhox#aJmH sH  hrh'#jJhrhox#UmH sH jhrhox#UmH sH hrhox#mH sH hrhox#aJhrhox#5aJhrhox#5"****ummQ$$IfkdƜ$$IfF40$4T  0644 laf4p ***+ummQ$$Ifkd$$IfF40$4T  0644 laf4p + ++Q+ummQ$$IfkdǞ$$IfF40$4T  0644 laf4p Q+R+b++ummQ$$Ifkd$$IfF40$4T  0644 laf4p +++, -umam # & F$IfQ$$IfkdE$$IfF40$4T  0644 laf4p  - -!-"-uldQ$$If Q$IfgdY kd$$IfF40$4T  0644 laf4p "-#-5-6-xppQ$$Ifkdá$$IfF0$4T  0644 lap 6-7-D-E-xppQ$$Ifkd|$$IfF0$4T  0644 lap E-F-G-Y-q-uqiiQ$$IfJkd5$$IfF40$4T  0644 laf4p m-n-o-p-r-}--------------.....s...011&1ú͖ͯͯ}p[p(jhrhox#0JH*UaJmH sH hrhox#aJmH sH hrh'mH sH hrhox#6]mH sH  hrh'#jrhrhox#UmH sH hrhox#mH sH hrhox#aJhrhox#5aJjhrhox#UmH sH !jhrhox#EHUmH sH #jK hrhox#UVmH sH q-r-}--ummQ$$Ifkd$$IfF40$4T  0644 laf4p ----ummQ$$Ifkd$$IfF40$4T  0644 laf4p ---.ummQ$$Ifkd$$IfF40$4T  0644 laf4p ....Q.ummQ$$Ifkd$$IfF40$4T  0644 laf4p Q.R.s.0ummQ$$Ifkdm$$IfF40$4T  0644 laf4p 0000uldQ$$If Q$Ifgd\kd,$$IfF40$4T  0644 laf4p 0000uldQ$$If Q$Ifgd\kd$$IfF40$4T  0644 laf4p 0000ummQ$$Ifkd$$IfF40$4T  0644 laf4p 011&1.1uqkcQ$$IfQ$IfJkdi$$IfF40$4T  0644 laf4p &1.101111111112222)2*2.2/22"3%3^3a3h3i33333,4-4E4F4444һ߫һߞsg\hrhox#nH tH hrhox#>*nH tH hrh%_HEmH sH hrhox#_HEmH o(sH hrhox#6]_HEmH sH hrhox#_HEmH sH j#hrhox#UaJ hrh'jhrhox#UaJjhrhox#UaJhrhox#aJhrhox#5aJhrhox#6\]aJ$.101F1L1ummQ$$Ifkd($$IfF40$4T  0644 laf4p L1N1r102ummQ$$Ifkd$$IfF40$4T  0644 laf4p 0212>2]2ummQ$$Ifkd$$IfF40$4T  0644 laf4p ]2^2n22ummQ$$Ifkd_$$IfF40$4T  0644 laf4p 222G4ummQ$$Ifkd$$IfF40$4T  0644 laf4p G4H4^4_4ummQ$$Ifkdݱ$$IfF40$4T  0644 laf4p _4`4r4s4ummQ$$Ifkd$$IfF40$4T  0644 laf4p s4t44_5ummQ$$Ifkd[$$IfF40$4T  0644 laf4p 4444444444444[5^5a5s5u5v555555555555566 6 66666666ɸӝӍӝӝvӝjhrhox#>*nH tH jԶhrhox#UaJ hrh'jWhrhox#UaJjhrhox#UaJhrhox#5aJmH sH !hrhox#6\]aJmH sH hrhox#5aJhrhox#aJhrh'nH tH hrhox#nH tH hrhox#6]nH tH )_5`5a5s5u5uqiiQ$$IfJkd$$IfF40$4T  0644 laf4p u5v555ummQ$$Ifkdٴ$$IfF40$4T  0644 laf4p 5556ummQ$$Ifkd$$IfF40$4T  0644 laf4p 666+6ummQ$$IfkdQ$$IfF40$4T  0644 laf4p +6,6<6_6ummQ$$Ifkd$$IfF40$4T  0644 laf4p _6`666ummQ$$Ifkdϸ$$IfF40$4T  0644 laf4p 6666ummQ$$Ifkd$$IfF40$4T  0644 laf4p 6666uogQ$$IfQ$IfkdM$$IfF40$4T  0644 laf4p 6667ummQ$$Ifkd $$IfF40$4T  0644 laf4p 6677#7%7*7/7077777777777777 8I8888888888ɾӱӡӱӏtfT"jhrhox#B*EHUphj J hrhox#UVhrhox#B*phjhrhox#B*Uphhrhox#mH sH  hrh'jhrhox#UaJjhrhox#UaJhrhox#6\]hrhox#5aJhrhox#aJhrh'nH tH hrhox#nH tH hrhox#6]nH tH 77777uqiiQ$$IfJkd˻$$IfF40$4T  0644 laf4p 7777ummQ$$Ifkd$$IfF40$4T  0644 laf4p 7777ummQ$$IfkdO$$IfF40$4T  0644 laf4p 77 8J8ummQ$$Ifkd$$IfF40$4T  0644 laf4p J8K8[8n8ummQ$$IfkdJ$$IfF40$4T  0644 laf4p n8o888uma Q$h$If^hQ$$Ifkd $$IfF40$4T  0644 laf4p 8888ummQ$$Ifkd$$IfF40$4T  0644 laf4p 8888ummQ$$Ifkd$$IfF40$4T  0644 laf4p 8888ummQ$$IfkdF$$IfF40$4T  0644 laf4p 88888uqkcQ$$IfQ$IfJkd$$IfF40$4T  0644 laf4p 8899ummQ$$Ifkd$$IfF40$4T  0644 laf4p 899&9'9=9>9N9O9S9T9c99;;;;;;;;;;;;;;;;<;<<<</=´{̍si[hrhox#\_HEnHtHhrhox#5\hrhox#5#j]hrhox#UmH sH jhrhox#UmH sH hrhox#mH sH hrhox#56]aJhrhox#6]mH sH hrhox#5aJ hrh'j)hrhox#UaJjhrhox#UaJ hrhox#hrhox#aJ"99&9U9ummQ$$Ifkdj$$IfF40$4T  0644 laf4p U9V9c99ummQ$$Ifkd$$IfF40$4T  0644 laf4p 9999ummQ$$Ifkde$$IfF40$4T  0644 laf4p 999:J;umgmQ$IfQ$$Ifkd$$$IfF40$4T  0644 laf4p J;K;a;b;ummQ$$Ifkd$$IfF40$4T  0644 laf4p b;c;u;v;ummQ$$Ifkd$$IfF40$4T  0644 laf4p v;w;;;ummQ$$Ifkda$$IfF40$4T  0644 laf4p ;;;;;uqh`Q$$If Q$Ifgd"1Jkd $$IfF40$4T  0644 laf4p ;;;;uldQ$$If Q$Ifgd"1kd$$IfF40$4T  0644 laf4p ;;;;ummQ$$Ifkd$$IfF40$4T  0644 laf4p ;;<<<ummQ$$Ifkd$$IfF40$4T  0644 laf4p <<=<M<`<ummQ$$Ifkd$$IfF40$4T  0644 laf4p `<a<<<uma Q$h$If^hQ$$IfkdX$$IfF40$4T  0644 laf4p <<<<ummQ$$Ifkd$$IfF40$4T  0644 laf4p <<<<ummQ$$Ifkd$$IfF40$4T  0644 laf4p <<<<ummQ$$Ifkd$$IfF40$4T  0644 laf4p <<<?@AAODu`[TEEE & F /x^/`#$ & F# & F# & F @ ^`gdM\kdT$$IfF40$4T  0644 laf4p /=1=>>AASCNDPDFFFEF~FFFFFFFG㢖ufWufE4 hrhn9PCJOJQJ^JaJ"hrh"15CJOJQJ\^Jhrh:CJOJQJ^Jhrh"1CJOJQJ^Jhrhox#CJOJQJ^J"hrhox#5CJOJQJ\^Jhrhox#\mH sH hrhox#5mH nH sH tH hrhox#nHtH hrhox#jhrhox#0JH*Uhrhox#6]_HEnHtHhrhox#_HEnHtHhrhox#5\_HEnHtHODFF;FEF]FeFjF}F$$ b $Ifa$$$If $$a$$a$#$ & F @ ^`gdM\# & F}F~FFFFFpGzrgrT9$ & F ==$If^=`gdM\$$ b $Ifa$gdn9P $$Ifgd:$$Ifkd$$IfTlF #M006    4 laTGG'H(H)H,HLHMH`JKKKKKKKKLLͻwk^RNG<4Rhox#nH tH hox#6]nH tH hox#6]hox#jhox#0JH*Uhox#\mH nHsH tHhox#CJOJQJ^Jh'hox#CJOJQJ^J hrhox#CJOJQJ^JaJ(hrhox#CJOJQJ^JaJmH sH hrhox#CJOJQJ^J"hrhox#5CJOJQJ\^J hrhQVCJOJQJ^JaJ hrhn9PCJOJQJ^JaJ hrh`DCJOJQJ^JaJpGG(H)H,H;HMH_WOG$$IfJ$If$$Ifkd$$IfTlF #M006    4 laT$ & F ==$If^=`gdM\MHyHHHHHI IaJ} & F ||\$7$8$H$If^|`\ $7$8$H$If^` & F $7$8$H$If` $7$8$H$If^` & F $7$8$H$If` $7$8$H$IfaJbJeJJJzrjj$$If$$Ifkd$$IfTlF #M006    4 laTJJJKKzrjj$$If$$Ifkd$$IfTlF #M006    4 laTKKKKKzrjj$$If$$Ifkd[$$IfTlF #M006    4 laTKKKLMMMN;OOOzuiiYiiiiiq7$8$H$^q` q^q`$a$kd$$IfTlF #M006    4 laT LMMMMMMMMMMMNNO.O;O @c112BYL%bpu UXRY7&meabM-VK-WMcPX\ > ]a*#3 1y&22@M`@&8sA##t] `p021)W2\ԡRYz] `J]$$If!vh55#v#v:V F t655Dd |J  C A? "2  !"#$%&'()*+,-./0123456789:;<=>?@ABCDEFGHIJKLMNOPQRSTUVWXYZ[\]^_`abcdefghijklmnopqrstuvwxyz{|}~      !"#$%&'()*+,-./0123456789:;<=>?@ABCDEFGHIJKLMNOPQRSTUVWXYZ[\]^_`abcdefghijklmnopqrstuvwxyz{|}~      !"#$%&'()*+,-./0123456789:;<=>?@ABCDEFGHIJKLMNOPQRSTUVWXYZ[\]^_`abcdefghijklmnopqrstuvwxyz{|}~8(Root Entry| FCfEData WordDocument{2ObjectPool~`fCf_1264598409OF`f`fOle CompObjfObjInfo "%(-0147:=@CFILOPQTWZ]`cfknoruvy| FMicrosoft Equation 3.0 DS Equation Equation.39q\(pt C BSL =C BSL,tree F#Microsoft Editor de ecuaciones 3Equation Native x_1241449438 FPQfPQfOle CompObj r.0 DS Equation Equation.39q"p C BSL FMicrosoft Equation 3.0 DS Equation Equation.39q:, C BSL,ObjInfo Equation Native  >_1264598417FPQfPQfOle  CompObj fObjInfoEquation Native V_1301753324|FP3 fP3 ftree FMicrosoft Equation 3.0 DS Equation Equation.39q / C BSL,tree,i =C BSL,AG/BG,i,tt=1tOle CompObjfObjInfoEquation Native  * " *4412*1year FMicrosoft Equation 3.0 DS Equation Equation.39qBpLO C BSL,tree,i_1264598445FP3 fP3 fOle CompObjfObjInfoEquation Native ^_1264598454FP3 fP3 fOle  CompObj !f FMicrosoft Equation 3.0 DS Equation Equation.39qN@U$l C BSL,AG/BG,i,t F#Microsoft Editor de ecuaciones 3ObjInfo!#Equation Native $j_1241449736 &$FP3 fP3 fOle &CompObj#%'rObjInfo&)Equation Native *)_1264598470,)FP3 fP3 f.0 DS Equation Equation.39q p i FMicrosoft Equation 3.0 DS Equation Equation.39q?k C BSL,Ole +CompObj(*,fObjInfo+.Equation Native /AG/BG,i,t =C G,i,t "C L,i,t FMicrosoft Equation 3.0 DS Equation Equation.39qN`ԫ C BSL,AG/BG,i,t_1264598476.FP3 fP3 fOle 2CompObj-/3fObjInfo05Equation Native 6j_1264598206S3FP3 fP3 fOle 8CompObj249f FMicrosoft Equation 3.0 DS Equation Equation.39q.: C G,i,t FMicrosoft Equation 3.0 DS EqObjInfo5;Equation Native <J_1264598212|8FP3 fP3 fOle >CompObj79?fObjInfo:AEquation Native BJ_1264837430=FP3 fP3 fuation Equation.39q.PYT; C L,i,t FMicrosoft Equation 3.0 DS Equation Equation.39qOle DCompObj<>EfObjInfo?GEquation Native HJ.` C L,i,t FMicrosoft Equation 3.0 DS Equation Equation.39q  C G,i,t = BSL,i *G_1264837110JBFP3 fP3 fOle JCompObjACKfObjInfoDMEquation Native N_1264598236GFP3 fP3 fOle RCompObjFHSf tree,j,i,t *CF jj=1J " FMicrosoft Equation 3.0 DS Equation Equation.39q.sLO C G,i,tObjInfoIUEquation Native VJ_1264837119LFP3 fP3 fOle X FMicrosoft Equation 3.0 DS Equation Equation.39q*  BSL,i FMicrosoft Equation 3.0 DS EqCompObjKMYfObjInfoN[Equation Native \F_1264598290EcQFP3 f@}fOle ^CompObjPR_fObjInfoSaEquation Native bZuation Equation.39q>9 G tree,j,i,t FMicrosoft Equation 3.0 DS Equation Equation.39q_1255511552wVFr'fr'fOle dCompObjUWefObjInfoXgEquation Native h:_1303277259[F@}f@}fOle iCompObjZ\jfP  CF j FMicrosoft Equation 3.0 DS Equation Equation.39qT¡P$ G tree,j,i,t =G w,j,i,t *(1+R 1  j )ObjInfo]lEquation Native m_1264572367?r`F@}f@}fOle p FMicrosoft Equation 3.0 DS Equation Equation.39q.œ<) G w,j,i,t =I V,j,i,t *D j *BEF 1,jCompObj_aqfObjInfobsEquation Native t_1264598360eF@}f@}fOle wCompObjdfxfObjInfogzEquation Native {Z FMicrosoft Equation 3.0 DS Equation Equation.39q>st G tree,j,i,t FMicrosoft Equation 3.0 DS Equation Equation.39q_1264572433jF@}f@}fOle }CompObjik~fObjInfol.2D G w,j,i,t FMicrosoft Equation 3.0 DS Equation Equation.39q(8l R 1  jEquation Native N_1290434894oF@}f@}fOle CompObjnpf      !#"$&%')*,+-/.02134576vw9:;<=>?@ABCDEFGHIJKLMNOPQRSTUVWXYZ[\]^_`abcdefghijklmnopqrstuxzy{}|~ObjInfoqEquation Native D_1264572444htF@}f@}fOle  FMicrosoft Equation 3.0 DS Equation Equation.39q.2  I V,j,i,tCompObjsufObjInfovEquation Native N_1255511957yFr'fr'fOle CompObjxzfObjInfo{Equation Native 6 FMicrosoft Equation 3.0 DS Equation Equation.39ql D j FMicrosoft Equation 3.0 DS Equation Equation.39q_1303277172!Y~F@}f@}fOle CompObj}fObjInfoEquation Native F_1264572456F@}f@}fOle CompObjfT*# C BB_tree,j,i,t =C AB_ObjInfoEquation Native _1264837174F@f@fOle tree,j,i,t *R j FMicrosoft Equation 3.0 DS Equation Equation.39qNyԆ C BSL,AG/BG,i,tCompObjfObjInfoEquation Native j_1300277567?F@f@fOle CompObjfObjInfoEquation Native F FMicrosoft Equation 3.0 DS Equation Equation.39q*, C j,i,t F#Microsoft Editor de ecuaciones 3_1241458341F@f@fOle CompObjrObjInfo.0 DS Equation Equation.39q" $dl T FMicrosoft Equation 3.0 DS Equation Equation.39q.JpIF C AB_trEquation Native )_1264572580F@f@fOle CompObjfObjInfoEquation Native f_1264572589F@f@fOle ee,j,i,t FMicrosoft Equation 3.0 DS Equation Equation.39q.Jx C BB_tree,j,i,tCompObjfObjInfoEquation Native f_1264837214F@f@fOle CompObjfObjInfoEquation Native F FMicrosoft Equation 3.0 DS Equation Equation.39q*T A BSL,i FMicrosoft Equation 3.0 DS Equation Equation.39q_1264572597F@_f@_fOle CompObjfObjInfo   !$'*-036;>ADGJMPQTWZ_dghkpuxyz{|.>pn  V tree,j,i,t FMicrosoft Equation 3.0 DS Equation Equation.39q| D jEquation Native Z_1255515300F@f@fOle CompObjfObjInfoEquation Native 6_1255515309Fr'fr'fOle  FMicrosoft Equation 3.0 DS Equation Equation.39q*| BEF 2,j FMicrosoft Equation 3.0 DS EqCompObj fObjInfo Equation Native  F_1255515362"^F@f@fOle CompObjfObjInfoEquation Native 6uation Equation.39qB R j FMicrosoft Equation 3.0 DS Equation Equation.39qJd  C AB_tr_1264575392]F@f@fOle CompObjfObjInfoEquation Native f_1264837227F@f@fOle CompObjfee,j,i,t FMicrosoft Equation 3.0 DS Equation Equation.39q. C AB_tree,j,i,t =A BSL,i *nTR j,i,t *CObjInfoEquation Native _126457266356F@f@fOle "F j *f j DBH,H() FMicrosoft Equation 3.0 DS Equation Equation.39q.J; C AB_tree,j,i,tCompObj#fObjInfo%Equation Native &f_1264837238F@f@fOle (CompObj)fObjInfo+Equation Native ,F FMicrosoft Equation 3.0 DS Equation Equation.39q*2 A BSL,i FMicrosoft Equation 3.0 DS EqE2J٭C3<= [`!SE2J٭C3<= V`0!xcdd``fd``baV d,FYzP1n:B@?b ؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u ,@RgfHIQj*LDr I<; Fe ng s>` R^Pt Ma(w b&ֽV .\D.v0o8^+KRsA<.f8Bg%]$$If!vh55#v#v:V F t655Dd \  c $A? ?#" `2l\XUI@H&`!@\XUI@F@$'xcdd``^$d@9`,&FF(`TARRcgbR x *,@=P5< %! 8 :@AbSR!K7S? `01d++&1]3@dH25*R 0Bg#1׊;HE }(|fVAT~ ; ;sB^ `"y`a*0TR cIE_[&X(FT" yF%` LJphh@ܕL wW&0;pi)0ה˙ tͽ:ĹS'H <$A \ \*ALE.+KRsA<.h)6Qj%Dd |J  C A? "2BNjǴk~ cB`![BNjǴk~ v `~ 0)xcdd``fd``baV d,FYzP1n:&6! KA?H1Z؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u ,@RF\籂d2+9/ %E0=&f )'bg?dv70MpF ~S4O:0Ff\PI@*\1E.] `p321)Wx ], 0O`qMxk]$$If!vh55#v#v:V F t655;Dd O|J  C A? "2~ M.`y`!q~ M.``0, 0?xcdd``bd``baV d,FYzP1n:! KA?H1Z l@P5< %! `3);aV&br2ua|4~*+odȣ wW&0;⎏+XY1TsA  v 0y{I)$5ba\~f.se]$$If!vh55#v#v:V F t655Dd \  c $A? ?#" `2>]T.UaS``!]T.UaS:Yxcdd`` @c112BYL%bpuiLn~WU)XͶw`v \Ll[ RlcrLߏyCn .qn;S?_5YZYT7z`iauL&:!" yia]"qǗ/s22224gM /_ a>;`-ofQ% r*&x¼o߁jW 4NJw=$Js9|;Dd O|J   C A ? "2Ybz|my`!qYbz|m`0, 0?xcdd``bd``baV d,FYzP1n:! KA?H1Z l@P5< %! `3);aV&brRua|a4~ +o`ȣ wW&0;ĈHK04~i b;j+KRsA<.gf8=r`$$If!vh55#v#v:V l6554Dd |J   C A ? " 2}gtG9*%EiY"`!QgtG9*%Eir@`0xcdd``dd``baV d,FYzP1n:&! KA?H1Z00sC0&dT20ͤ `[YB2sSRsR~  @29@ڈJfLI%/gL {%ľ?m`T\14u᣻U {+ss@q$V .\ D.v0o8+KRsA<.'f8ja`$$If!vh55#v#v:V l6554Dd |J   C A ? " 2|{T1,,[%`!S|{T1,,r `d0!xcdd``dd``baV d,FYzP1n:&! KA?H1Z؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u ,@RF\{A2%0o&?}*!5#>F0no2Jt0pxw&\P V .\ D.v0o8+KRsA<.'f8.jDd |J   C A ? " 2]Xyn,Rn[0'`!S]Xyn,Rnr `d0!xcdd``dd``baV d,FYzP1n:&! KA?H1Z؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u ,@RF\{A2%0o&?}*!5#>F0no2Jt0pxw&\P$V .\ D.v0o8+KRsA<.'f8Yj`$$If!vh55#v#v:V l6554Dd \   c $A? ?#" ` 2>]T.UaS)`!]T.UaS:Yxcdd`` @c112BYL%bpu a,`! @!A hca>̮ `2Pxcdd``gb``baV d,FYzP1n:! KA?H1Yzjx|K2B* R>t/ @201W&0;qq]ػK1 f3`Ƞ pi#LZ\ 3/kv/͵;/r'\F LYA*+aR=0(ސbr<a/?^0YPaT;~Ώ3c|P%E08:`*1YN>p+v`~&/ia5d?+mpvÒ(`{ `[ S8_̇@10AX,E5IB >>4gss? `pyĤ\Y\ te[1Dd |J  C A? "2~}9+0%Z,/`!R}9+0%r@`0 xcdd``dd``baV d,FYzP1n:&! KA?H1Z00sC0&dT20ͤ `[YB2sSRsR~  @29@ڈJfLI%/gL {%ľ?m`T\14u᣻U {+ssͼ\'uHK%4v1KsF&&\p,{jf$$If!vh55#v#v:V l46554f4Dd X|J  C A? "2rzԃ0b6XN1`!Fzԃ0b6X`0xcdd`` @c112BYL%bpu60d#d;& ` e\PH⚏s60:0T8sAÉ ]=gdbR ,.I@XP`qhrUf$$If!vh55#v#v:V l46554f4Dd |J  C A? "2s+Q;]s>oO(4`!G+Q;]s>o<``\0xcdd``cd``baV d,FYzP1n:,B@?b X؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u @Ct mђ$SR /g3|A0?7gPR qA?\?]R^3}1o`)hyL>4q1v0o8+KRsA<.,#c#3XR`)]$$If!vh55#v#v:V F t655Dd |J  C A? "2R @b*T{iZ.6`!& @b*T{iZ㪒`@C0xcdd``> @c112BYL%bpu Ę!9|;FJRSS#E1 RT㋰p%%2 Ma(w O\60jTh ".h>)=Ĥ\Y\ te;mތDd c |J  C A? "2.]J-!><`!.]J-!>`0xcdd``~ @c112BYL%bpu o_„ᣇ(! -[>{@W&0;ܸ^ , \|+]=Ĥ\Y\ teDd |J  C A? "2s+Q;]s>oOA?`!G+Q;]s>o<``\0xcdd``cd``baV d,FYzP1n:,B@?b X؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u @Ct mђ$SR /g3|A0?7gPR qA?\?]R^3}1o`)hyL>4q1v0o8+KRsA<.,#c#3XR`)f$$If!vh55#v#v:V l46554f4 Dd |J  C A? "2n6|kuPDT<JA`!B6|kuPDT<:`@20xcdd``ed``baV d,FYzP1n:&! KA?H1Z؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u ,@RF\sA2%0C&?|Mg?#wGH{%H\F Ӂ * # e.pL@LE;F&&\, _yf$$If!vh55#v#v:V l46554f4Dd hJ  C A? "2P Qik#,.D`!$ Qik#@|hxcdd`` @c112BYL%bpu @c112BYL%bpuF0no2Jt0pxw&\Pp:N@*\*A.] `p321)Wx ], 0O`qk2}DyK _Ref226785241Dd D|J  C A? "2plr|50,s>^L4V`!Dlr|50,s>^:`0xcdd``ed``baV d,FYzP1n:B@?b ؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u ,@RF\A2%0~ _d*!7#~F0F7b _s; `炆28& B"#RpeqIj.ebl~d0_Dd |J  C A? "2J=03s)Bn[BX`!SJ=03s)Bnr `d0!xcdd``dd``baV d,FYzP1n:&! KA?H1Z؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u ,@RF\{A2%0o&?}*!5#>F0no2Jt0pxw&\P(R!V .\ D.v0o8+KRsA<.'f8jDd |J   C A? "2cLq Sr[_Z`!ScLq Srr `d0!xcdd``dd``baV d,FYzP1n:&! KA?H1Z؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u ,@RF\{A2%0o&?}*!5#>F0no2Jt0pxw&\PxX[1TTrAc ]=8gdbR ,.I@X`okDd l J ! C A? " 2^2MOJ(㉼:|\`!22MOJ(㉼xcdd``a 2 ĜL0##0KQ* W@XRcgbR a PT obIFHeA*/&*de-:At/DX+ss\\U뾔71#XLF]F\?qdVBS<1.V1psY:@*l6#\5хB_bo`$ 7$37X/\!(?718H1U ?`\+`~&*^U}=/<_#g`gGV| a|ѝcbi!#'1 Í_cIq?pB0 :p AT9^T y;*_ !%/`z#/ $p1 悖!\rb nv0odbdbR ,.I 0p)3XY?rDd | |J " C A? "!2sj|?VWLtx_`!sj|?VWLt``h{0xڝK@]IjD:`v-l1B"?pOp*8 NBq)$ԃ˽ݻ˽w@H`KEAUfќ)Ţ20:%QXWb1#'{Q]=v@U`Z۳݁}'0#䉮w|S.pu/^w& _ٕBuئQ֔#w͸Ƥ%y,x8W<V8S~z2=cs[3ńs jGE%yxHS*8ox)GFAb]9~]-n2.VOJgv2jЍX&4]?qeWwN 4e~ @޹mNJc戊[MG∙T2RD kfUZU+,u9~0/ӤXgg.՚WtCwrm/DBQ[?c:ߎpW˄,='b滞.W1I=K7LV;Dd O|J % C A!? "$2qݲXE݈yPg`!qqݲXE݈`0, 0?xcdd``bd``baV d,FYzP1n:! KA?H1Z l@P5< %! `3);aV&brRua|a4~ +o`ȣ wW&0;8?+ `.hrD.v0o8021)Wx ], 0`q s<]$$If!vh55#v#v:V F t655Dd |\ & c $A"? ?#" `%2a}d&2Kcxr=i`!5}d&2Kcxr `0xcdd``ed``baV d,FYzP1n:&f! KA?H1Zjـ7$# lo&`'0L ZZǰw͗c@Vg$u m $SR  GYg#Q¹ $b.#?`ݿ炆"8!@``㆑I)$5b2B16?1Z]$$If!vh55#v#v:V F t655Dd \ ' c $A#? ?#" `&2? xf<'ϖ>Zl`! xf<'ϖ>:`!xcdd`` @c112BYL%bpug#11 $b.#> 悆8,! v 0y{Ĥ\Y\ te!V]$$If!vh55#v#v:V F t655Dd |J + C A'? "*2r)RߟW/|K;Nu`!F)RߟW/|K;<`0xcdd``cd``baV d,FYzP1n:! KA?H1Z, l@P5< %! `3);aV&br)e1L>4q1v0o8+KRsA<.,#c#3XS_`]$$If!vh55#v#v:V F t655Dd T|J , C A(? "+2QpQթ])e[Vf-lx`!%pQթ])e[Vf `XJ0xcdd``> @c112BYL%bpu \HIz`!A> \H``P0xcdd`` @c112BYL%bpu @c112BYL%bpu @c112BYL%bpu-Wab8fm%9LLJ% H X3Xl5Dd $|J 2 C A$? "12&'Bl?h;]`!U&'Bl?h;\`HD 0#xcdd``cd``baV d,FYzP1n:lB@?b ؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u ,@RF\@2%0~)+ ?e*9|Af %E0^ O9:A\<1p501T8;DBe؇:N0;qA W[ n``cI)$5b2B16?3WcEa$$If!vh55#v#v:V Fn t655Dd 0|J 3 C A&? "22]HM4sLm9m`!1HM4sLm`k0xcdd`` @c112BYL%bpug#11 $b.#> 悆8,! v 0_1264572671F@_f@_fOle .CompObj/fObjInfo1uation Equation.39q.2> nTR j,i,t FMicrosoft Equation 3.0 DS Equation Equation.39qEquation Native 2N_1255520741F@_f@_fOle 4CompObj5fObjInfo7Equation Native 8:_1261896650F@_f@_fOle 9X+d CF j FMicrosoft Equation 3.0 DS Equation Equation.39q*>2 f j DBH,H()CompObj:fObjInfo<Equation Native =Z_1264837375F@_f@_fOle ?CompObj@fObjInfoBEquation Native CJ FMicrosoft Equation 3.0 DS Equation Equation.39q.Pd  C L,i,t FMicrosoft Equation 3.0 DS Equation Equation.39q_1262412675l F@_f0fOle ECompObj  FfObjInfo H}/ C BSL =0 FMicrosoft Equation 3.0 DS Equation Equation.39q>j%| C ACTU; Equation Native IK_1258265197TF0f0fOle KCompObjLfObjInfoNEquation Native O_1255522819IF%f%fOle RAL =C P "GHG E FMicrosoft Equation 3.0 DS Equation Equation.39q22\ C ACTUALCompObjSfObjInfoUEquation Native VN_1244105587wF0f0fOle XCompObjYfObjInfo[Equation Native \: FMicrosoft Equation 3.0 DS Equation Equation.39q,) C P F#Microsoft Editor de ecuaciones 3.0 DS Equation Equation.39q_1227015608!F0f0fOle ]CompObj^rObjInfo `7"pd GHG E FMicrosoft Equation 3.0 DS Equation Equation.39q0 C P =C t *4412 t=Equation Native a>_1301753438#F0f0fOle bCompObj"$cfObjInfo%eEquation Native f_1247314138(F0f0fOle i1t* " *1year FMicrosoft Equation 3.0 DS Equation Equation.39q&l C P FMicrosoft Equation 3.0 DS EqCompObj')jfObjInfo*lEquation Native m:_1258265773-F0f0fOle nCompObj,.ofObjInfo/qEquation Native r:uation Equation.39q>(\  C t FMicrosoft Equation 3.0 DS Equation Equation.39qC C t =_1259156891h2F0f0fOle sCompObj13tfObjInfo4vEquation Native w__12591569357F df dfOle }CompObj68~f(C AG,i,t +C BG,i,t +C DW,i,t +C LI,i,t +C SOC,i,t ) i=1M PS " FMicrosoft Equation 3.0 DS Equation Equation.39qObjInfo9Equation Native N_1259156944<F df dfOle 2P \ C AG,i,t FMicrosoft Equation 3.0 DS Equation Equation.39q2`4$  C BG,iCompObj;=fObjInfo>Equation Native N_1259156954:AF0f0f,t FMicrosoft Equation 3.0 DS Equation Equation.39q2845 C DW,i,tOle CompObj@BfObjInfoCEquation Native N_1259156964FF0f0fOle CompObjEGfObjInfoH FMicrosoft Equation 3.0 DS Equation Equation.39q2fF C LI,i,t FMicrosoft Equation 3.0 DS Equation Equation.39qEquation Native N_1257942315:KF0f0fOle CompObjJLfObjInfoMEquation Native R_1264572840SbPF0f0fOle f6?, C SOC,i,t FMicrosoft Equation 3.0 DS Equation Equation.39q.>.t V l,j,iCompObjOQfObjInfoREquation Native Z_1264572717XUF0f0f,sp,t FMicrosoft Equation 3.0 DS Equation Equation.39q.$ C AB_tree,l,j,i,sp,t =V l,j,i,sp,t "D Ole CompObjTVfObjInfoWEquation Native  j "BEF 2,j "CF j FMicrosoft Equation 3.0 DS Equation Equation.39q.^\  C AB_tree,l,j,i,sp,t_1264572803ZF0f0fOle CompObjY[fObjInfo\Equation Native z_1264572875_F0f0fOle CompObj^`f FMicrosoft Equation 3.0 DS Equation Equation.39q. ^0 C BB_tree,l,j,i,sp,t =C AB_tree,l,j,i,sp,t "R jObjInfoaEquation Native _1264572888]gdF0f0fOle  FMicrosoft Equation 3.0 DS Equation Equation.39q.^Ph  C BB_tree,l,j,i,sp,t FMicrosoft Equation 3.0 DS EqCompObjcefObjInfofEquation Native z_1264572917iF0f0fOle CompObjhjfObjInfokEquation Native zuation Equation.39q.^x;$8 C AB_tree,l,j,i,sp,t FMicrosoft Equation 3.0 DS Equation Equation.39q_1262590246nF df dfOle CompObjmofObjInfopEquation Native 6_1264572977sF0f0fOle CompObjruf(} R j FMicrosoft Equation 3.0 DS Equation Equation.39qc  .  &G & MathTypeObjInfoOlePres000tvEquation Native _1263121348yF0f0f-HHzTimes New Romanww 0wdfn-2 py2  Ny2 f ly2 ly2 py 2 Uijke2 Imj 2 btree2 G BB2 pB 2 :ijke2 .mj 2 Gtree2 ,BBTimes New Romanww 0wdfn-2  AB2 K CB2 0CB@Times New Romanww 0wdfn-2 \ pB 2 \ ijke2 \ mjTimes New Romanww 0wdfn- 2 10000@Times New Romanww 0wdfn-2 \c ,02 \W ,0Times New Romanww 0wdfn-2 q,02 q,02  ,02 ,02 _02 V,02 ,02 ,02 _0Symbol ww 0wdfn-2 q02 =0Symbol ww 0wdfn-2  0 & "Systemndfn !-.z0 C tree,i,sp,t =(C AB_tree,l,j,i,sp,tl=1N j,i,sp,t " j=1S PS " +C BB_tree,l,j,i,sp,t ) FMicrosoft Equation 3.0 DS Equation Equation.39qBt C tree,Ole CompObjxzfObjInfo{Equation Native ^i,sp,t FMicrosoft Equation 3.0 DS Equation Equation.39qc  .  &G & MathType_1264572943N~F0f0fOle CompObj}fObjInfoOlePres000Equation Native  z_1264572955F0f0fOle      !#&)*+,/258;>ADEFILOTWZ]^_behknqrstuvwxyz{|}~-HHzTimes New Romanww 0wdfn-2 py2  Ny2 f ly2 ly2 py 2 Uijke2 Imj 2 btree2 G BB2 pB 2 :ijke2 .mj 2 Gtree2 ,BBTimes New Romanww 0wdfn-2  AB2 K CB2 0CB@Times New Romanww 0wdfn-2 \ pB 2 \ ijke2 \ mjTimes New Romanww 0wdfn- 2 10000@Times New Romanww 0wdfn-2 \c ,02 \W ,0Times New Romanww 0wdfn-2 q,02 q,02  ,02 ,02 _02 V,02 ,02 ,02 _0Symbol ww 0wdfn-2 q02 =0Symbol ww 0wdfn-2  0 & "Systemndfn !-.^ 7 C AB_tree,l,j,i,sp,t FMicrosoft Equation 3.0 DS EqCompObjfObjInfoEquation Native z_1264572966F f fuation Equation.39q.^P\<_ C BB_tree,l,j,i,sp,t FMicrosoft Equation 3.0 DS Equation Equation.39qOle CompObjfObjInfoOlePres000D"{  .  @& & MathTypep@Times New Romanww 0wfk-2  py 2 ijke2 mjTimes New Romanww 0wfk-2 `HNj@Times New Romanww 0wfk-2 ,j2 ,j & "Systemkfk !-.7R0  N j,i,sp,t FMicrosoft Equation 3.0 DS Equation Equation.39qEquation Native "S_1290935208F0f0fOle $CompObj%fObjInfo'Equation Native (_1263121447F df dfOle -| C tree,i,t =A i A sp  i C tree,i,sp,tsp=1P i " FMicrosoft Equation 3.0 DS Equation Equation.39qCompObj.fObjInfo0Equation Native 1V_1263121452wF0f0f:`*t C tree,i,t FMicrosoft Equation 3.0 DS Equation Equation.39qBh@4+ C tree,Ole 3CompObj4fObjInfo6Equation Native 7^i,sp,t FMicrosoft Equation 3.0 DS Equation Equation.39q,H A sp  i_1290935238JF f fOle 9CompObj:fObjInfo<Equation Native =H_1264572994qF0f0fOle ?CompObj@f FMicrosoft Equation 3.0 DS Equation Equation.39q.  C AB_tree,j,i,sp,t =f j (DBH,H)*CF jl=1N j,sp "ObjInfoBEquation Native C_1264573003F0f0fOle GCompObjHfObjInfoJEquation Native Kr_1262591707EF0f0f FMicrosoft Equation 3.0 DS Equation Equation.39q.V`$( C AB_tree,j,i,sp,t FMicrosoft Equation 3.0 DS Equation Equation.39qOle MCompObjNfObjInfoPEquation Native Q:(`)$ CF j FMicrosoft Equation 3.0 DS Equation Equation.39q(7`4* f j (DBH,H)_1262591766F0f0fOle RCompObjSfObjInfoUEquation Native VS_1264573014F0f0fOle XCompObjYf FMicrosoft Equation 3.0 DS Equation Equation.39q.¾h7 C BB_tree,j,i,sp,t =C AB_tree,j,i,sp,t "R jObjInfo[Equation Native \_1264573026F0f0fOle ` FMicrosoft Equation 3.0 DS Equation Equation.39q.V($ C BB_tree,j,i,sp,t FMicrosoft Equation 3.0 DS EqCompObjafObjInfocEquation Native dr_12645730591F0f0fOle fCompObjgfObjInfoiEquation Native jruation Equation.39q.V27 C AB_tree,j,i,sp,t FMicrosoft Equation 3.0 DS Equation Equation.39q_1264573116F0f0fOle lCompObjmfObjInfooOlePres000pEquation Native <_1264510675vF0f dfOle c  .  &G & MathType-HHzTimes New Romanww 0wdfn-2 py2  Ny2 f ly2 ly2 py 2 Uijke2 Imj 2 btree2 G BB2 pB 2 :ijke2 .mj 2 Gtree2 ,BBTimes New Romanww 0wdfn-2  AB2 K CB2 0CB@Times New Romanww 0wdfn-2 \ pB 2 \ ijke2 \ mjTimes New Romanww 0wdfn- 2 10000@Times New Romanww 0wdfn-2 \c ,02 \W ,0Times New Romanww 0wdfn-2 q,02 q,02  ,02 ,02 _02 V,02 ,02 ,02 _0Symbol ww 0wdfn-2 q02 =0Symbol ww 0wdfn-2  0 & "Systemndfn !-. (_; C tree,i,sp,t =(C AB_tree,j,i,sp,t +C BB_tree,j,i,sp,tj=1S PS " ) FMicrosoft Equation 3.0 DS Equation Equation.39qCompObjfObjInfoEquation Native ^_1264573131F df dfBx C tree,i,sp,t FMicrosoft Equation 3.0 DS Equation Equation.39qc  .  &     v#!"$%'&()*,+-./0123546789:<=[?>C@ABDEFIGHJKLMNOQPRTSUVWXY\Z]^_a`bcdfegihjklnmopqsrtwxyz{|}~y{Ĥ\Y\ te!Va$$If!vh55#v#v:V F_ t655Dd |J 4 C A,? "32i52Sֳ9Eˌ`!=52Sֳ9`0 xcdd``cd``baV d,FYzP1n:! KA?H1Z, l@P5< %! `3);aV&br @c112BYL%bpubG`8qA  v 0y{I)$5b2B16?0zDa$$If!vh55#v#v:V F} t655a$$If!vh55#v#v:V F} t655a$$If!vh55#v#v:V F} t655a$$If!vh55#v#v:V F} t655Dd |J 7 C A'? "62r)RߟW/|K;NL`!F)RߟW/|K;<`0xcdd``cd``baV d,FYzP1n:! KA?H1Z, l@P5< %! `3);aV&br)e1L>4q1v0o8+KRsA<.,#c#3XS_`Dd |J 8 C A.? "72h@Uh=R,[\`!Sh@Uh=R,r `d0!xcdd``dd``baV d,FYzP1n:&! KA?H1Z؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u ,@RF\{A2%0o&?}*!5#>F0no2Jt0pxw&\PeM@*\*A.] `p321)Wx ], 0O`qjDd hJ 9 C A/? "82}?A,zrP|Yy`!Q?A,zrP|T@@8 |xcdd``bd``baV d,FYzP1n:&&6! KA?H1Z10< UXRY7S?&,e`abM-VK-WMcػK1 +`0``@6j` dTb1 d^penR~CP 0v$sY@*l+a|+j=$b#(>`4bb}R}@ɘ>P .pAtA``cI)$5ba\`je)>Dd hJ : C A0? "92f{__!dU-7|`!tf{__!dU-7`@@|Bxcdd``6`d``baV d,FYzP1n:&&~! KA?H1Z30< UXRY7&meabM-VK-WMcػK1 f3``@6zXq9AJ.(ߒ rt u<; 'F3nf =*"0B6dspenR~CP K o!632UЅۣYA|[8ߊ" .p|AlMaF&&\,B,_Dd hJ ; C A1? ":2zh|mVҝ`!Nh|m@ |xcdd`` @c112BYL%bpu @c112BYL%bpu c $A4? ?#" `=2 N3<: ˆ`!N3<: ˆ8@@1xcdd``a 2 ĜL0##0KQ* W d3H1)fYA< #3PT obIFHeA*/&`b]F"L L9A,a +L *'] ZZǰw͗c@Vg5c#`^HejbTD9Wf!6*'F&0 b/k, %P{3@?`@0>g w01Ra,n_ _  I|`wj 1>y`!Ԟa\PXMo2)6ceB3kk%7ap38"c\|1v0o8221)Wx\|t$HeDd TJ ? C A5? ">2b. VT3>X`!6. VT3 XJxcdd`` @c112BYL%bpuM 1nHK%4T!KkF&&\, Rf$$If!vh5G5 #vG#v :V l46554f4Dd hJ @ C A6? "?2b~: h@@>`!6~: h@@@@C|xcdd`` @c112BYL%bpu UXRY7&meabM-VK-WMcػK1 f3``@6z)< `1ܤr;.\7׊¥ *\%5#RpeqIj.ebl~`*BSTf$$If!vh5G5 #vG#v :V l46554f4f$$If!vh5G5 #vG#v :V l46554f4f$$If!vh5G5 #vG#v :V l46554f47Dd lJ A C A7? "@2칠Y/4^ru`!m칠Y/4^rT#`7P;xڥkAL6MզMM)ڪT `lS/BB)/œ=BAOk/"{30!Yv>fA 6|%qƢaR"Ɔ.7M8 >Wu#iRլ|CZ?IOqQnqp~qZln}in!\0(ޗ|ȇ@?ͤLo?Fױސȷ/߹{wJ_viTp yV13^͘a3~%mƛ)3[>X"GgvNK6q-b( 75d<q&/~*Rr48;}K(5gkWNtG#?:\=elk kR}r`X,+~8n70 D8Bt>TMr&7&L+I=n3YD9߯e;m\ۅk/iu$ezy]$$If!vh5[5 #v[#v :V F t655Dd |J B C A8? "A2Tiԏs07\`!TTiԏs07r`0"xcdd``dd``baV d,FYzP1n:,B@?b 00sC0&dT20ͤ `[YB2sSRsR~  29@ڈ H gL ';CkG}`Fe ` saG/e*=I9 x"V .\ D.v0o8+KRsA<.'f8hh]$$If!vh5[5 #v[#v :V F t655Dd |J C C A9? "B2@Abprx0\ `!T@Abprx0r``\0"xcdd``dd``baV d,FYzP1n:,B@?b X؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u @Ct mю$SR a3|&!5#>F0no2gwt0p_τ*=I9 PG@*\ܹA.] `p321)Wx ], 0O`q*j]$$If!vh5[5 #v[#v :V F t655Dd 4|J D C A:? "C2 #Cv[Sj2\`!T #Cv[Sj2r `p0"xcdd``dd``baV d,FYzP1n:&V! KA?H1ZX؀깡jx|K2B* R vfRv,L ! ~ Ay {|)?Č`u @Ct m$SR c3|]&]!5#>F0no2pt0pof*=I9 X V p8! v 0y{qĤ\Y\ t0.?1i]$$If!vh5[5 #v[#v :V F t655Dd |J E C A;? "D2vQl [`!SvQl r`0!xcdd``dd``baV d,FYzP1n:! KA?H1Z, l@P5< %! `3);aV&brg#Ql'?H\Fրݯ KAEȞܤr-bp8! v 0y{qĤ\Y\ t0.?1h]$$If!vh5[5 #v[#v :V F t655Dd H|J F C A<? "E2[{V5Je]`!U[{V5Jet@`"0#xcdd``bd``baV d,FYzP1n:&V! KA?H1ZT UXRYP7&meabM-VK-WMcػK1 f3``@6z$SR kP&3 y62p&8D@e93~Pd Ma(w lj V .\!D.v0o8+KRsA<.'f8j?]$$If!vh5[5 #v[#v :V F t655]$$If!vh5[5 #v[#v :V F t655]$$If!vh5[5 #v[#v :V F t655Dd |P G S A=? "F2yVSρ&V,./U`!MVSρ&V,./Z`0xcdd``ed``baV d,FYzP1n:! KA?H1Z, l@P5< %! `3);aV&br? "G2XGգ'X>*`!XGգ'X>*F`'0xڥӻK@.i$FC} (Z] 覭jPgqrrE͵`\#(bEAu]Rdo3E\u&nb~aVr ś~L6Ճl4)U`e %tjɭRoj7*eN )67eYwczT)7 <]C0'|"=^>w+8!Kގ5c[b$>yWҺՖDĺ1Ǫ\Go b ,(Bm5|\o͌M `Ĵe6dE v;gi|G ~%*f~4dehB6Ug3Va'~ cFP/7Rx/<Dd (|P I S A?? "H2 'կZ SlNt`!l 'կZ SlN@` 0:xcdd``cd``baV d,FYzP1n:&! KA?H1Zq00sC0&dT20ͤ `[YB2sSRsR~  X.4&vLI%?d%Cqτ+XA,8+ S 2l()JMbqq?\?]R $\FxCD gCfEs+XPL ~4q q `p`dbR ,.I@XP-Lkak`$$If!vh55#v#v:V l6554Dd |P J S A=? "I2yVSρ&V,./U:`!MVSρ&V,./Z`0xcdd``ed``baV d,FYzP1n:! KA?H1Z, l@P5< %! `3);aV&br