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Citation: Sonneveld BGJS. Testing the Experts. Ann Agric Crop Sci. 2018; 3(1): 1032.Ann Agric Crop Sci - Volume 3 Issue 1 - 2018
ISSN: 2573-3583 | www.austinpublishinggroup.com
Sonneveld. © All rights are reserved
Annals of Agricultural & Crop Sciences
Open Access
Reporting on consistency compares, for identical sites, the frequency
of similar expert judgments and detailed specification on one or more
class deviations [8].
Reproducibility
The relationship between expert assessments and a set of
explanatory variables is formalized by estimating a qualitative
response model. Land degradation is represented by an unknown
continuous variable y and related to independent variables x.
Assuming additive error terms the underlying process is
represented as:
yi
= β′ xi
+ εi
,			 (1)
where i are observations, β the parameters to be estimated
and εi
the disturbance, independent across observations. Ordered
land degradation classes are observed as zi
. Adjacent intervals of yi
correspond with qualitative information zi
, as follows:
zi
= 1 		 if yi
< µ1
,
zi
= 2 		 if µ1
≤ yi
< µ,	 (2)
M
zi
= n 		 if µn-1
≤ yi
.
Disturbances εi
of the probability model are assumed to possess a
logistic distribution, leading to a cumulative logistic transformation
function Λ, with explicit form: 1+ e−1 (µi
− β X).
Parameters β and thresholds (µ1
,….., µn-1
) are simultaneously
estimated by maximizing probability of a correct classification by
experts. Significance of estimated parameters is tested by Chi-square
statistics while a likelihood ratio tests overall quality of the estimation.
Accuracy of the estimated model is evaluated by a hit ratio, the
percentage of correctly predicted observations, while a 10-fold cross-
validation verifies model robustness for inclusion or exclusion of
observations.
Interpretability
Boundaries of the ordered qualitative response models can
be quantified by using real-valued process data [9] as independent
variables in the above described estimation against expert classes
as dependent variables. The estimation expresses qualitative class
boundaries into quantitative values generated by the degradation
process. Specifically, by default, cut- off points of expert classes is
equal to the cumulative probability value of 0.5. Hence, we can define:
1 i
0.5 and where
1 ( )
x x
e i X B
µ µ
µ
= =
+ − µ −β
Expresses threshold values µi
in physical units of the degradation
process.
Key Role
Formalizing expert assessments plays a key role in addressing
land degradation hazard. Expert judgments can be collected fast and
Short Communication
In absence of reliable models and prevailing data paucity expert
judgments constitute a valuable alternative for land degradation
assessments. Yet, these qualitative expert opinions are branded
as subjective and non-reproducible as tests for consistency are
missing and qualitative classes remain difficult to interpret. This
communication summarizes formal procedures to test expert
judgment for consistency, reproducibility while correlation with
quantitative data makes qualitative judgments interpretable.
Land Degradation
Devastatingeffectsoflanddegradationonnaturalresourcequality,
landscape heritages and ecology have far reaching consequences for
current and future human well-being [1]. The cry for action to curb
the catastrophic effects of land degradation at national scale, the level
where most decisions on land use take place, seem, therefore, justified
[2]. Yet, assessing degradation processes at larger scale is not an easy
task. Despite vast resources spent on development of degradation
models there are hitherto no reliable quantitative assessment
methods available to prioritize interventions at regional or national
scale. The main reason is the chaotic [3] and highly unpredictable
nature of the degradation process that is influenced by many factors,
some of which are poorly understood [4]. Indeed absence of dense
and long term monitoring networks impede explanation of the year-
to-year variation of land degradation in its geographical dependence
of natural resources and land use [5]. Instead land degradation
assessments increasingly resort on qualitative expert opinions [6]
that express the state of land degradation in ordered qualitative
classes [7]; information that is easy to collect and inexpensive. Yet,
principal criticism on uniformity, reproducibility and interpretability
permeate these assessments and this communication aims to address
these concerns and by introducing tests for consistency, formalizing
the relationship between expert judgments and explanatory variables
and quantifying boundaries of the qualitative assessments.
Consistency
Consistency can be tested by comparing expert judgments
on land degradation for similar combinations of spatially explicit
information on biophysical conditions, land use and where available
socio-economic information. In practice, these attributes are
categorized and spatially overlaid to identify map units (of analysis)
that are unique in their combination of spatial attributes. The state
of degradation for obtained combinations is assessed by experts.
Short Communication
Testing the Experts
Sonneveld BGJS*
Amsterdam Centre for World Food Studies/Athena
Institute, Vrije Universiteit Amsterdam, Netherlands
*Corresponding author: Sonneveld BGJS, Amsterdam
Centre for World Food Studies/Athena Institute, Vrije
Universiteit Amsterdam, Netherlands
Received: February 16, 2018; Accepted: March 01,
2018; Published: March 08, 2018
Ann Agric Crop Sci 3(1): id1032 (2018) - Page - 02
Sonneveld BGJS Austin Publishing Group
Submit your Manuscript | www.austinpublishinggroup.com
relativelycheapwhileformaltestprocedurescanstrengthentheexpert
capacity to ensure that assessments are applied with confidence.
References
1.	 Sustainable Development Knowledge Platform. Sustainable Development.
2018.
2.	 UNCCD. Global land outlook - Key messages. United Nations Convention to
Combat Desertification. 2017.
3.	 Philips JD. Deterministic chaos in surface runoff. 1992.
4.	 Bastola S, Dialynas YG, Bras RL, Noto LV, Istanbulluoglu E. The role of
vegetation on gully erosion stabilization at a severely degraded landscape:
A case study from Calhoun Experimental Critical Zone Observatory.
Geomorphology. 2018; 308: 25-39.
5.	 Vanmaercke M, Poesen J, Van Mele B, Demuzere M, Bruynseels A, Golosov
V. How fast do gully headcuts retreat? Earth-Science Reviews. 2016; 154:
336-355.
6.	 Blanco PD, Hardtke LA, Rostagno CM, Del Valle HF, Metternicht GI.
Soil Degradation in Peninsula Valdes: Causes, Factors, Processes, and
Assessment Methods. Late Cenozoic of Península Valdés, Patagonia,
Argentina. 2017; 191-213.
7.	 Abrahams D. Overland Flow: Hydraulics and Erosion Mechanics. 1992.
8.	 Sonneveld BGJS, Bai Z, Ndiaye DS, Bindraban PS. Comparing Rainfall Use
Efficiency Trends with Expert Judgments for Nation-Wide Land Degradation
Assessments: The Case of Senegal. Journal of Sustainable Development.
2012; 5: 116-135.
9.	 Greene WH. Econometric Analysis. 1991.
Citation: Sonneveld BGJS. Testing the Experts. Ann Agric Crop Sci. 2018; 3(1): 1032.Ann Agric Crop Sci - Volume 3 Issue 1 - 2018
ISSN: 2573-3583 | www.austinpublishinggroup.com
Sonneveld. © All rights are reserved

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Annals of Agricultural & Crop Sciences

  • 1. Citation: Sonneveld BGJS. Testing the Experts. Ann Agric Crop Sci. 2018; 3(1): 1032.Ann Agric Crop Sci - Volume 3 Issue 1 - 2018 ISSN: 2573-3583 | www.austinpublishinggroup.com Sonneveld. © All rights are reserved Annals of Agricultural & Crop Sciences Open Access Reporting on consistency compares, for identical sites, the frequency of similar expert judgments and detailed specification on one or more class deviations [8]. Reproducibility The relationship between expert assessments and a set of explanatory variables is formalized by estimating a qualitative response model. Land degradation is represented by an unknown continuous variable y and related to independent variables x. Assuming additive error terms the underlying process is represented as: yi = β′ xi + εi , (1) where i are observations, β the parameters to be estimated and εi the disturbance, independent across observations. Ordered land degradation classes are observed as zi . Adjacent intervals of yi correspond with qualitative information zi , as follows: zi = 1 if yi < µ1 , zi = 2 if µ1 ≤ yi < µ, (2) M zi = n if µn-1 ≤ yi . Disturbances εi of the probability model are assumed to possess a logistic distribution, leading to a cumulative logistic transformation function Λ, with explicit form: 1+ e−1 (µi − β X). Parameters β and thresholds (µ1 ,….., µn-1 ) are simultaneously estimated by maximizing probability of a correct classification by experts. Significance of estimated parameters is tested by Chi-square statistics while a likelihood ratio tests overall quality of the estimation. Accuracy of the estimated model is evaluated by a hit ratio, the percentage of correctly predicted observations, while a 10-fold cross- validation verifies model robustness for inclusion or exclusion of observations. Interpretability Boundaries of the ordered qualitative response models can be quantified by using real-valued process data [9] as independent variables in the above described estimation against expert classes as dependent variables. The estimation expresses qualitative class boundaries into quantitative values generated by the degradation process. Specifically, by default, cut- off points of expert classes is equal to the cumulative probability value of 0.5. Hence, we can define: 1 i 0.5 and where 1 ( ) x x e i X B µ µ µ = = + − µ −β Expresses threshold values µi in physical units of the degradation process. Key Role Formalizing expert assessments plays a key role in addressing land degradation hazard. Expert judgments can be collected fast and Short Communication In absence of reliable models and prevailing data paucity expert judgments constitute a valuable alternative for land degradation assessments. Yet, these qualitative expert opinions are branded as subjective and non-reproducible as tests for consistency are missing and qualitative classes remain difficult to interpret. This communication summarizes formal procedures to test expert judgment for consistency, reproducibility while correlation with quantitative data makes qualitative judgments interpretable. Land Degradation Devastatingeffectsoflanddegradationonnaturalresourcequality, landscape heritages and ecology have far reaching consequences for current and future human well-being [1]. The cry for action to curb the catastrophic effects of land degradation at national scale, the level where most decisions on land use take place, seem, therefore, justified [2]. Yet, assessing degradation processes at larger scale is not an easy task. Despite vast resources spent on development of degradation models there are hitherto no reliable quantitative assessment methods available to prioritize interventions at regional or national scale. The main reason is the chaotic [3] and highly unpredictable nature of the degradation process that is influenced by many factors, some of which are poorly understood [4]. Indeed absence of dense and long term monitoring networks impede explanation of the year- to-year variation of land degradation in its geographical dependence of natural resources and land use [5]. Instead land degradation assessments increasingly resort on qualitative expert opinions [6] that express the state of land degradation in ordered qualitative classes [7]; information that is easy to collect and inexpensive. Yet, principal criticism on uniformity, reproducibility and interpretability permeate these assessments and this communication aims to address these concerns and by introducing tests for consistency, formalizing the relationship between expert judgments and explanatory variables and quantifying boundaries of the qualitative assessments. Consistency Consistency can be tested by comparing expert judgments on land degradation for similar combinations of spatially explicit information on biophysical conditions, land use and where available socio-economic information. In practice, these attributes are categorized and spatially overlaid to identify map units (of analysis) that are unique in their combination of spatial attributes. The state of degradation for obtained combinations is assessed by experts. Short Communication Testing the Experts Sonneveld BGJS* Amsterdam Centre for World Food Studies/Athena Institute, Vrije Universiteit Amsterdam, Netherlands *Corresponding author: Sonneveld BGJS, Amsterdam Centre for World Food Studies/Athena Institute, Vrije Universiteit Amsterdam, Netherlands Received: February 16, 2018; Accepted: March 01, 2018; Published: March 08, 2018
  • 2. Ann Agric Crop Sci 3(1): id1032 (2018) - Page - 02 Sonneveld BGJS Austin Publishing Group Submit your Manuscript | www.austinpublishinggroup.com relativelycheapwhileformaltestprocedurescanstrengthentheexpert capacity to ensure that assessments are applied with confidence. References 1. Sustainable Development Knowledge Platform. Sustainable Development. 2018. 2. UNCCD. Global land outlook - Key messages. United Nations Convention to Combat Desertification. 2017. 3. Philips JD. Deterministic chaos in surface runoff. 1992. 4. Bastola S, Dialynas YG, Bras RL, Noto LV, Istanbulluoglu E. The role of vegetation on gully erosion stabilization at a severely degraded landscape: A case study from Calhoun Experimental Critical Zone Observatory. Geomorphology. 2018; 308: 25-39. 5. Vanmaercke M, Poesen J, Van Mele B, Demuzere M, Bruynseels A, Golosov V. How fast do gully headcuts retreat? Earth-Science Reviews. 2016; 154: 336-355. 6. Blanco PD, Hardtke LA, Rostagno CM, Del Valle HF, Metternicht GI. Soil Degradation in Peninsula Valdes: Causes, Factors, Processes, and Assessment Methods. Late Cenozoic of Península Valdés, Patagonia, Argentina. 2017; 191-213. 7. Abrahams D. Overland Flow: Hydraulics and Erosion Mechanics. 1992. 8. Sonneveld BGJS, Bai Z, Ndiaye DS, Bindraban PS. Comparing Rainfall Use Efficiency Trends with Expert Judgments for Nation-Wide Land Degradation Assessments: The Case of Senegal. Journal of Sustainable Development. 2012; 5: 116-135. 9. Greene WH. Econometric Analysis. 1991. Citation: Sonneveld BGJS. Testing the Experts. Ann Agric Crop Sci. 2018; 3(1): 1032.Ann Agric Crop Sci - Volume 3 Issue 1 - 2018 ISSN: 2573-3583 | www.austinpublishinggroup.com Sonneveld. © All rights are reserved