Methodological Guide to Forensic Hydrology
Abstract
:1. Introduction
2. Environmental Rights
PRINCIPLE 15. To preserve the environment, the Precautionary Approach shall be widely applied by States according to their capabilities. Where there are threats of considerable or irreversible damage, the absence of sufficient scientific certainty should be unused as a reason for deferring cost-effective measures to prevent environmental degradation. This Principle comprises three critical components. (i) The mission to identify the hazard, (ii) risk management and identification of damage, and (iii) the existence of scientific uncertainty.
3. Forensic Hydrology
3.1. Perfect Research and Contradictions
3.2. Fundamentals of Forensic Ethics
4. Criminalistic Investigation and Its Principles
4.1. The Declaration of Sydney
- Activity and presence produce traces that are fundamental vectors of information.
- Scene investigation is a scientific and diagnostic endeavour requiring scientific expertise.
- Forensic science is case-based and reliant on scientific knowledge, investigative methodology and logical reasoning.
- Forensic science is an assessment of findings in context due to time asymmetry.
- Forensic science deals with a continuum of uncertainties.
- Forensic science has multi-dimensional purposes and contributions.
- Forensic science findings acquire meaning in context.
4.2. Field Forensics
4.3. Lab Forensics
4.4. Basic Principles of Forensic Investigation
Forensic Science Crime | Sydney Declaration | Forensic-Hydrology |
---|---|---|
1. Principle of use. During the occurrence of a disaster or environmental crime, the participation of mechanical, physical, chemical, biological, hydraulic, and meteorological. agents is inevitable. These agents must be identified in the initial working hypothesis (Analogical Hypothesis). | ||
1. Principle of production. The activity and presence of agents produce traces and indications that are fundamental vectors of information, identification and possible reconstruction. | 2. Principle of production. Once at least one of the agents has acted, evidence (tracks or marks) is produced. According to the agent represent the evidence, this has an extraordinary etiological significance and scientific properties that support the research. | |
1. Principle of exchange. The French criminologist Edmund Locard (1910) observed that every criminal leaves a part of him-self at the crime scene and takes something with him. These traces can lead to his identity, since there is inevitably an exchange of evidence between the criminal, the victim and the scene. | 1. Principle of exchange. No activities can take place without preserving traces. They are followed or carried away (Locard’s exchange maxim). The nature of the activity influences the types of elements exchanged. The trace represents a vector of information capable of being detected, recovered, examined and interpreted. | 3. Principle of exchange. The agent inevitably leaves a trace of his personal identity with the victim and at the scene of a disaster or environmental crime. This recognizes a bi-univocal axiom exchange of evidence. Based on the first two Principles, the exchange hypothesis (inductive hypothesis) is formulated. What could represent the evidence that should be identified or verified in the field? |
4. Principle of recognition. This research will lead to the identification of the cause or agent and the reconstruction of the dynamics of the disaster or environmental crime. It is based on a deductive hypothesis built on verifiable facts. | ||
2. Principle of correspondence of characteristics. There is a logical relationship between the evidence collected at the scene and the probable perpetrator, i.e., they correspond to each other. | 2. Principle of correspondence. It is the one that allows deducing, from matching or correlations, the similarity of a trace left by a certain agent or object at the scene of the crime. It is to deduce and to reason under uncertainty, the reconstruction of an event through the study of traces. | 5. Principle of correspondence. Based on the first four Principles, it is possible to attribute responsibility for the disaster or environmental crime to at least one of the positively identified agents. The Principle of Correspondence concludes with the identification of the agent or agents who have acted to cause the disaster or environmental crime. |
3. Principle of reconstruction. From the evidence collected, the data provided during the investigation and the testimony of witnesses to the event, a realistic reproduction is possible. | 3. Principle of reconstruction. Traces represent signs. The formulation of pertinent questions, critical thinking, logical reasoning and the deductive, inductive and analogical process allow the reconstruction of a fact. | 6. Principle of reconstruction. The comparative analysis of the identified evidence collected, studied and associated with the disaster or environmental crime provides the qualitative, quantitative and analogical data. That makes possible the systematic reconstruction of the manner in which the disaster or environmental crime occurred. |
4. Principle of probability. According to the results acquired in the criminal research. It is possible to determine what represents the probability in which they occurred, and who or who participated in the facts. | 4. Principle of probability. No event can be determined with certainty. The circumstances that involve a trace can only evaluate the relative-value of the findings. The quality of the trace could be incomplete, imperfect or degraded. This increases the uncertainty and temporal asymmetry of the findings. It is therefore necessary to evaluate their probability of occurrence in time. | 7. Principle of probability. Here begins what is known as the argumentation stage. If the probability of an event happening is zero means that the event never takes place (falsity). If means that the event always occurs (certainty). At that point, a post-fact hypothesis must be constructed from the most probable facts. |
5. Uncertainty Principle. Forensic science faces with a continuum of doubts that are present at every step of the process. It is necessary to identify and quantify these uncertainties. Subjectivity can be accepted because it is recognized that uncertainty will never be eliminated. | 8. Uncertainty principle. There is a theory of untruth. That is, the subjectivity or uncertainty in the verification of facts. At that point a Null hypothesis must be constructed, which refutes the relationship between the facts and explains the uncertainty of the truth. | |
6. Principle of certainty. Forensic science has multi-dimensional objectives and contributions. The systematic study of traces makes it possible to establish certainties that recognize the facts and support decision-making in legal proceedings. | 9. Principle of certainty. At this stage the hypotheses must be confirmed or rejected. By employing scientific knowledge, the forensic hydrologist obtains results that fall within certitude (certainty). That allows the conclusion that the evidence collected is associated with the participation of agents who acted, in a certain place, to cause the disaster or environmental crimes. | |
7. Conclusion Principle. Forensic scientists should defend their findings and opinions as appropriate, while acknowledging any meritorious alternatives. | 10. Conclusion principle. A scientific resolution should be presented. The conclusion should answer the questions associated with each stage of the research: detection, localization, chronology, identification and reconstruction (see Table 2). All conclusions should include quantification of uncertainty. |
Type of Information | Forensic Science | Medicine | Forensic Hydrology |
---|---|---|---|
Detection | Did a crime happen? What are the relevant trace(s) that can be detected? | Is a person suffering from a health problem? What are the relevant symptom(s) that can be detected? | Has a disaster, environmental crime or environmental damage happened? Who or what caused the event? What effects did the event cause? (Direct and indirect). |
Localization | Where is the trace(s) at the scene? | Where is the symptom(s) on/in the human body? | Where did the event happen or was it triggered? What agent(s) caused the event? Why did the incident happen? What are the relevant evidences about the event? |
Chronology | When were the traces generated and in which sequence? | When did the symptoms first appear, and how did they evolve? | When did the disaster, environmental crime, or damage occur? When did it happen? |
Identification | Who/what is the source of a trace? | What is the source of a symptom? | What evidence should be collected and preserved in relation to the event? |
Reconstruction | What activities may have caused the generation of the traces? | What activities/lifestyle may be contributing to the observed symptom(s)? | Why are the events treated as a disaster, an environmental crime or damage to the environment? |
5. Decalogue of Forensic-Hydrology and Its Application
5.1. Principle of Use
5.2. Principle of Production
5.3. Principle of Exchange
5.4. Recognition Principle
5.5. Principle of Correspondence
5.6. Reconstruction Principle
5.7. Principle of Probability
5.8. Uncertainty Principle
5.9. Principle of Certainty
5.10. Conclusion Principle
Agent, Dimensions and Usual Units | Regimen | Estimated and Required Action for Hazard Analysis |
---|---|---|
Flow and flood 1 | Flood water depth (y) | |
Flood duration | ||
Flood water velocity (v) | ||
Water sedimentation | ||
Return period of flow () | ||
Rainfall and hailstorm 2 | Rainfall height (hp) | |
Rainfall height in 24 h () | ||
Rain rate also known as precipitation intensity (R) | ||
IDF curves magnitude-duration-frequency | ||
Return period of rainfall () | ||
Debris and debris-flow 3 | Debris flow hazard recognition | |
Estimation of debris flow probability | ||
Regimen production of debris flow (volume and frequency) | ||
Volume of the initiating failure | ||
Volumes entrained along the transport reach | ||
Estimation of volumes deposited along the transport reach | ||
Landslide 4 | Landslide type (by origin) and height | |
Landslide direction / movement type | ||
Landslide velocity | ||
Landslide impact pressure and soil material |
6. Discussion
7. Conclusions
Supplementary Materials
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
Appendix A
Profile View (m) | Plan View (m) | ||||
---|---|---|---|---|---|
High | Model Length | Prototype Length | High | Model Length | Prototype Length |
C | 0.755 | 22.65 | A | 0.155 | 4.65 |
E | 10.38 | 311.4 | V | 1.765 | 52.95 |
Appendix B
Year | Flow | Ordered Event | Order | Return Period (Year) | Probability of Occurrence |
---|---|---|---|---|---|
1993 | 1660.0 | 3800.0 | 1 | 30.00 | 0.03 |
1994 | 618.0 | 2280.0 | 2 | 15.00 | 0.07 |
1995 | 876.0 | 1660.0 | 3 | 10.00 | 0.10 |
1996 | 563.0 | 1410.0 | 4 | 7.50 | 0.13 |
1997 | 824.0 | 1230.0 | 5 | 6.00 | 0.17 |
1998 | 557.0 | 1150.0 | 6 | 5.00 | 0.20 |
1999 | 917.0 | 1120.0 | 7 | 4.29 | 0.23 |
2000 | 683.0 | 1030.0 | 8 | 3.75 | 0.27 |
2001 | 740.0 | 934.0 | 9 | 3.33 | 0.30 |
2002 | 520.0 | 921.0 | 10 | 3.00 | 0.33 |
2003 | 824.0 | 917.0 | 11 | 2.73 | 0.37 |
2004 | 818.0 | 876.0 | 12 | 2.50 | 0.40 |
2005 | 3800.0 | 824.0 | 13 | 2.31 | 0.43 |
2006 | 934.0 | 824.0 | 14 | 2.14 | 0.47 |
2007 | 1120.0 | 818.0 | 15 | 2.00 | 0.50 |
2008 | 360.0 | 779.0 | 16 | 1.88 | 0.53 |
2009 | 1230.0 | 740.0 | 17 | 1.76 | 0.57 |
2010 | 1030.0 | 683.0 | 18 | 1.67 | 0.60 |
2011 | 1410.0 | 658.0 | 19 | 1.58 | 0.63 |
2012 | 779.0 | 618.0 | 20 | 1.50 | 0.67 |
2013 | 610.0 | 610.0 | 21 | 1.43 | 0.70 |
2014 | 1150.0 | 581.0 | 22 | 1.36 | 0.73 |
2015 | 522.0 | 563.0 | 23 | 1.30 | 0.77 |
2016 | 418.0 | 557.0 | 24 | 1.25 | 0.80 |
2017 | 2280.0 | 522.0 | 25 | 1.20 | 0.83 |
2018 | 921.0 | 520.0 | 26 | 1.15 | 0.87 |
2019 | 367.0 | 418.0 | 27 | 1.11 | 0.90 |
2020 | 658.0 | 367.0 | 28 | 1.07 | 0.93 |
2021 | 581.0 | 360.0 | 29 | 1.03 | 0.97 |
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Order Number m | Observed Value | Return Period Tr (Years) | Probability of Occurrence |
---|---|---|---|
1 | x1 | n + 1 | 1/(n + 1) |
2 | x2 | (n + 1)/2 | 2/(n + 1) |
m | xm | (n + 1)/m | m/(n + 1) |
n − 1 | xn−1 | (n + 1)/(n − 1) | (n − 1)/(n + 1) |
n | xn | (n + 1)/n | n/(n + 1) |
Damage State-Factor Range [Damage or Risk] | Rain Rate R (mm h−1) [Rainfall Height hp] (mm 24 h−1) | Hazard Flow–Velocity (m s−1) [Landslide Velocity] | Hazard Flow Depth y (m) [Flood Duration] | Jointly Flow Depth y (m) and Flow Velocity v (m s−1) | Safe for … [Expected Damage] |
---|---|---|---|---|---|
Slight-very slow (0–1) [1%] | | | | & | All save [Not damage] |
Light-low-slow (1–10) [5%] | | | | & | Cars and able bodied adults [Water and sediment-laden water ingresses building’s main floor or basement] |
Moderate-medium (10–30) [20%] | | 1 | ] | 1& | Heavy vehicles and wading for adults [Lost related to wet furniture and some supporting elements damaged] |
Heavy-high-fast (30–60) [45%] | | | | & | Light constructions [Furniture wet, broken windows and doors are reported] |
Major-very high-very fast (60–100) [80%] | | | | & | Heavy constructions [Everything get wet and damage to crucial building-supporting piles and walls] |
Destroyed-extreme-extremely fast (100) [100%] | | | | & | Nothing [Structure is completely damaged or destroyed] |
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Gutierrez-Lopez, A. Methodological Guide to Forensic Hydrology. Water 2022, 14, 3863. https://doi.org/10.3390/w14233863
Gutierrez-Lopez A. Methodological Guide to Forensic Hydrology. Water. 2022; 14(23):3863. https://doi.org/10.3390/w14233863
Chicago/Turabian StyleGutierrez-Lopez, Alfonso. 2022. "Methodological Guide to Forensic Hydrology" Water 14, no. 23: 3863. https://doi.org/10.3390/w14233863
APA StyleGutierrez-Lopez, A. (2022). Methodological Guide to Forensic Hydrology. Water, 14(23), 3863. https://doi.org/10.3390/w14233863