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1.
Arch Toxicol ; 97(6): 1813-1822, 2023 06.
Article in English | MEDLINE | ID: mdl-37029818

ABSTRACT

The 1958 Delaney amendment to the Federal Food Drug and Cosmetics Act prohibited food additives causing cancer in animals by appropriate tests. Regulators responded by adopting chronic lifetime cancer tests in rodents, soon challenged as inappropriate, for they led to very inconsistent results depending on the subjective choice of animals, test design and conduct, and interpretive assumptions. Presently, decades of discussions and trials have come to conclude it is impossible to translate chronic animal data into verifiable prospects of cancer hazards and risks in humans. Such conclusion poses an existential crisis for official agencies in the US and abroad, which for some 65 years have used animal tests to justify massive regulations of alleged human cancer hazards, with aggregated costs of $trillions and without provable evidence of public health advantages. This article addresses suitable remedies for the US and potentially worldwide, by critically exploring the practices of regulatory agencies vis-á-vis essential criteria for validating scientific evidence. According to this analysis, regulations of alleged cancer hazards and risks have been and continue to be structured around arbitrary default assumptions at odds with basic scientific and legal tests of reliable evidence. Such practices raise a manifold ethical predicament for being incompatible with basic premises of the US Constitution, and with the ensuing public expectations of testable truth and transparency from government agencies. Potential remedies in the US include amendments to the US Administrative Procedures Act, preferably requiring agencies to justify regulations compliant with the Daubert opinion of the Daubert ruling of the US Supreme Court, which codifies the criteria defining reliable scientific evidence. International reverberations are bound to follow what remedial actions may be taken in the US, the origin of current world regulatory procedures to control alleged cancer causing agents.


Subject(s)
Neoplasms , Public Health , Animals , Humans , United States , Carcinogens/toxicity , Neoplasms/chemically induced , Neoplasms/prevention & control
2.
Arch Toxicol ; 95(9): 3133-3136, 2021 09.
Article in English | MEDLINE | ID: mdl-34363510

ABSTRACT

The EU chemicals strategy for sustainability (CSS) asserts that both human health and the environment are presently threatened and that further regulation is necessary. In a recent Guest Editorial, members of the German competent authority for risk assessment, the BfR, raised concerns about the scientific justification for this strategy. The complexity and interdependence of the networks of regulation of chemical substances have ensured that public health and wellbeing in the EU have continuously improved. A continuous process of improvement in consumer protection is clearly desirable but any initiative directed towards this objective must be based on scientific knowledge. It must not confound risk with other factors in determining policy. This conclusion is fully supported in the present Commentary including the request to improve both, data collection and the time-consuming and bureaucratic procedures that delay the publication of regulations.


Subject(s)
Public Health/legislation & jurisprudence , Risk Assessment/legislation & jurisprudence , European Union , Hazardous Substances/toxicity , Health Policy/legislation & jurisprudence , Humans
5.
J Toxicol Environ Health A ; 83(13-14): 485-494, 2020 07 17.
Article in English | MEDLINE | ID: mdl-32552445

ABSTRACT

Theoretically, both synthetic endocrine-disrupting chemicals (S-EDCs) and natural (exogenous and endogenous) endocrine-disrupting chemicals (N-EDCs) can interact with endocrine receptors and disturb hormonal balance. However, compared to endogenous hormones, S-EDCs are only weak partial agonists with receptor affinities several orders of magnitude lower than S-EDCs. Thus, to elicit observable effects, S-EDCs require considerably higher concentrations to attain sufficient receptor occupancy or to displace natural hormones and other endogenous ligands. Significant exposures to exogenous N-EDCs may result from ingestion of foods such as soy-based diets, green tea, and sweet mustard. While their potencies are lower as compared to natural endogenous hormones, they usually are considerably more potent than S-EDCs. Effects of exogenous N-EDCs on the endocrine system were observed at high dietary intakes. A causal relation between their mechanism of action and these effects is established and biologically plausible. In contrast, the assumption that the much lower human exposures to S-EDCs may induce observable endocrine effects is not plausible. Hence, it is not surprising that epidemiological studies searching for an association between S-EDC exposure and health effects have failed. Regarding testing for potential endocrine effects, a scientifically justified screen should use in vitro tests to compare potencies of S-EDCs with those of reference N-EDCs. When the potency of the S-EDC is similar or smaller than that of the N-EDC, further testing in laboratory animals and regulatory consequences are not warranted.


Subject(s)
Endocrine Disruptors/chemical synthesis , Endocrine Disruptors/toxicity , Environmental Exposure/analysis , Endocrine Disruptors/metabolism , Endocrine System/drug effects , Endocrine System/physiology , Environmental Exposure/statistics & numerical data , Feedback, Physiological/drug effects , Hormones/metabolism , Humans , Protein Binding , Receptors, Cell Surface/metabolism , Risk Assessment , Toxicity Tests/standards
6.
Arch Toxicol ; 94(7): 2549-2557, 2020 07.
Article in English | MEDLINE | ID: mdl-32514609

ABSTRACT

Theoretically, both synthetic endocrine disrupting chemicals (S-EDCs) and natural (exogenous and endogenous) endocrine disrupting chemicals (N-EDCs) can interact with endocrine receptors and disturb hormonal balance. However, compared to endogenous hormones, S-EDCs are only weak partial agonists with receptor affinities several orders of magnitude lower. Thus, to elicit observable effects, S-EDCs require considerably higher concentrations to attain sufficient receptor occupancy or to displace natural hormones and other endogenous ligands. Significant exposures to exogenous N-EDCs may result from ingestion of foods such as soy-based diets, green tea and sweet mustard. While their potencies are lower as compared to natural endogenous hormones, they usually are considerably more potent than S-EDCs. Effects of exogenous N-EDCs on the endocrine system were observed at high dietary intakes. A causal relation between their mechanism of action and these effects is established and biologically plausible. In contrast, the assumption that the much lower human exposures to S-EDCs may induce observable endocrine effects is not plausible. Hence, it is not surprising that epidemiological studies searching for an association between S-EDC exposure and health effects have failed. Regarding testing for potential endocrine effects, a scientifically justified screen should use in vitro tests to compare potencies of S-EDCs with those of reference N-EDCs. When the potency of the S-EDC is similar or smaller than that of the N-EDC, further testing in laboratory animals and regulatory consequences are not warranted.


Subject(s)
Dietary Exposure/adverse effects , Endocrine Disruptors/adverse effects , Endocrine System/drug effects , Phytochemicals/adverse effects , Toxicity Tests , Animals , Endocrine Disruptors/chemical synthesis , Endocrine System/metabolism , Endocrine System/physiopathology , Humans , Ligands , Risk Assessment
7.
Chem Biol Interact ; 326: 109099, 2020 Aug 01.
Article in English | MEDLINE | ID: mdl-32370863

ABSTRACT

Theoretically, both synthetic endocrine disrupting chemicals (S-EDCs) and natural (exogenous and endogenous) endocrine disrupting chemicals (N-EDCs) can interact with endocrine receptors and disturb hormonal balance. However, compared to endogenous hormones, S-EDCs are only weak partial agonists with receptor affinities several orders of magnitude lower. Thus, to elicit observable effects, S-EDCs require considerably higher concentrations to attain sufficient receptor occupancy or to displace natural hormones and other endogenous ligands. Significant exposures to exogenous N-EDCs may result from ingestion of foods such as soy-based diets, green tea and sweet mustard. While their potencies are lower as compared to natural endogenous hormones, they usually are considerably more potent than S-EDCs. Effects of exogenous N-EDCs on the endocrine system were observed at high dietary intakes. A causal relation between their mechanism of action and these effects is established and biologically plausible. In contrast, the assumption that the much lower human exposures to S-EDCs may induce observable endocrine effects is not plausible. Hence, it is not surprising that epidemiological studies searching for an association between S-EDC exposure and health effects have failed. Regarding testing for potential endocrine effects, a scientifically justified screen should use in vitro tests to compare potencies of S-EDCs with those of reference N-EDCs. When the potency of the S-EDC is similar or smaller than that of the N-EDC, further testing in laboratory animals and regulatory consequences are not warranted.


Subject(s)
Endocrine Disruptors/adverse effects , Endocrine System/drug effects , Environmental Exposure/adverse effects , Environmental Pollutants/adverse effects , Animals , Humans
8.
Toxicol In Vitro ; 67: 104861, 2020 Sep.
Article in English | MEDLINE | ID: mdl-32360643

ABSTRACT

Theoretically, both synthetic endocrine disrupting chemicals (S-EDCs) and natural (exogenous and endogenous) endocrine disrupting chemicals (N-EDCs) can interact with endocrine receptors and disturb hormonal balance. However, compared to endogenous hormones, S-EDCs are only weak partial agonists with receptor affinities several orders of magnitude lower. Thus, to elicit observable effects, S-EDCs require considerably higher concentrations to attain sufficient receptor occupancy or to displace natural hormones and other endogenous ligands. Significant exposures to exogenous N-EDCs may result from ingestion of foods such as soy-based diets, green tea and sweet mustard. While their potencies are lower as compared to natural endogenous hormones, they usually are considerably more potent than S-EDCs. Effects of exogenous N-EDCs on the endocrine system were observed at high dietary intakes. A causal relation between their mechanism of action and these effects is established and biologically plausible. In contrast, the assumption that the much lower human exposures to S-EDCs may induce observable endocrine effects is not plausible. Hence, it is not surprising that epidemiological studies searching for an association between S-EDC exposure and health effects have failed. Regarding testing for potential endocrine effects, a scientifically justified screen should use in vitro tests to compare potencies of S-EDCs with those of reference N-EDCs. When the potency of the S-EDC is similar or smaller than that of the N-EDC, further testing in laboratory animals and regulatory consequences are not warranted.


Subject(s)
Endocrine Disruptors/toxicity , Environmental Exposure , Environmental Pollutants/toxicity , Hormones/metabolism , Endocrine System , Humans , Receptors, Cell Surface/metabolism , Risk Assessment
10.
Food Chem Toxicol ; 142: 111349, 2020 Aug.
Article in English | MEDLINE | ID: mdl-32360905

ABSTRACT

Theoretically, both synthetic endocrine disrupting chemicals (S-EDCs) and natural (exogenous and endogenous) endocrine disrupting chemicals (N-EDCs) can interact with endocrine receptors and disturb hormonal balance. However, compared to endogenous hormones, S-EDCs are only weak partial agonists with receptor affinities several orders of magnitude lower. Thus, to elicit observable effects, S-EDCs require considerably higher concentrations to attain sufficient receptor occupancy or to displace natural hormones and other endogenous ligands. Significant exposures to exogenous N-EDCs may result from ingestion of foods such as soy-based diets, green tea and sweet mustard. While their potencies are lower as compared to natural endogenous hormones, they usually are considerably more potent than S-EDCs. Effects of exogenous N-EDCs on the endocrine system were observed at high dietary intakes. A causal relation between their mechanism of action and these effects is established and biologically plausible. In contrast, the assumption that the much lower human exposures to S-EDCs may induce observable endocrine effects is not plausible. Hence, it is not surprising that epidemiological studies searching for an association between S-EDC exposure and health effects have failed. Regarding testing for potential endocrine effects, a scientifically justified screen should use in vitro tests to compare potencies of S-EDCs with those of reference N-EDCs. When the potency of the S-EDC is similar or smaller than that of the N-EDC, further testing in laboratory animals and regulatory consequences are not warranted.


Subject(s)
Dietary Exposure , Endocrine Disruptors/toxicity , Environmental Pollutants/toxicity , Humans , Risk Assessment
11.
Environ Toxicol Pharmacol ; 78: 103396, 2020 Aug.
Article in English | MEDLINE | ID: mdl-32391796

ABSTRACT

Theoretically, both synthetic endocrine disrupting chemicals (S-EDCs) and natural (exogenous and endogenous) endocrine disrupting chemicals (N-EDCs) can interact with endocrine receptors and disturb hormonal balance. However, compared to endogenous hormones, S-EDCs are only weak partial agonists with receptor affinities several orders of magnitude lower. Thus, to elicit observable effects, S-EDCs require considerably higher concentrations to attain sufficient receptor occupancy or to displace natural hormones and other endogenous ligands. Significant exposures to exogenous N-EDCs may result from ingestion of foods such as soy-based diets, green tea and sweet mustard. While their potencies are lower as compared to natural endogenous hormones, they usually are considerably more potent. Effects of exogenous N-EDCs on the endocrine system were observed at high dietary intakes. A causal relation between their mechanism of action and these effects is established and biologically plausible. In contrast, the assumption that the much lower human exposures to S-EDCs may induce observable endocrine effects is not plausible. Hence, it is not surprising that epidemiological studies searching for an association between S-EDC exposure and health effects have failed. Regarding testing for potential endocrine effects, a scientifically justified screen should use in vitro tests to compare potencies of S-EDCs with those of reference N-EDCs. When the potency of the S-EDC is similar or smaller than that of the N-EDC, further testing in laboratory animals and regulatory consequences are not warranted.


Subject(s)
Biological Products/toxicity , Endocrine Disruptors/toxicity , Environmental Pollutants/toxicity , Endocrine System/drug effects , Environmental Exposure , Hormones , Humans , Receptors, Steroid/metabolism , Risk Assessment
13.
Regul Toxicol Pharmacol ; 97: A1-A3, 2018 Aug.
Article in English | MEDLINE | ID: mdl-30017904

ABSTRACT

Several recent and prominent articles in Science and Nature deliberately mischaracterized the nature of genuine scientific evidence. Those articles take issue with the United States Environmental Protection Agency's recent proposal to structure its policies and rules only from studies with transparently published raw data. The articles claim it is an effort to obfuscate with transparency, by eliminating a host of studies not offering raw data. A remarkable declaration by a Science editorial is that properly trained experts can verify the scientific evidence of studies without access to raw data, We assert the Agency's proposal must be sustained. Transparency in reporting is a fundamental ethical imperative of objective scientific research justifying massive official regulations and policies. Putative hazards bereft of independent scientific evidence will continue to stoke public anxieties, calling for precautionary regulations and policies. These should rely not on spurious science but on transparent tradeoffs between the smallest exposures compatible with utility and with social perceptions of affordable precaution.


Subject(s)
Government Agencies/organization & administration , Policy Making , Animals , Humans , United States , United States Environmental Protection Agency
15.
Toxicology ; 371: 12-16, 2016 Sep 14.
Article in English | MEDLINE | ID: mdl-27639665

ABSTRACT

A public appeal has been advanced by a large group of scientists, concerned that science has been misused in attempting to quantify and regulate unmeasurable hazards and risks.1 The appeal recalls that science is unable to evaluate hazards that cannot be measured, and that science in such cases should not be invoked to justify risk assessments in health, safety and environmental regulations. The appeal also notes that most national and international statutes delineating the discretion of regulators are ambiguous about what rules of evidence ought to apply. Those statutes should be revised to ensure that the evidence for regulatory action is grounded on the standards of the scientific method, whenever feasible. When independent scientific evidence is not possible, policies and regulations should be informed by publicly debated trade-offs between socially desirable uses and social perceptions of affordable precaution. This article explores the premises, implications and actions supporting the appeal and its objectives.


Subject(s)
Health/legislation & jurisprudence , Health/standards , Legislation as Topic/standards , Risk Assessment/legislation & jurisprudence , Risk Assessment/standards , Safety/legislation & jurisprudence , Safety/standards , Science/legislation & jurisprudence , Science/standards , Toxicology/legislation & jurisprudence , Toxicology/standards , Animals , Disease Models, Animal , Humans
16.
Toxicology ; 371: A1, 2016 09 14.
Article in English | MEDLINE | ID: mdl-27381659

Subject(s)
Public Policy
18.
Toxicol Sci ; 146(1): 11-5, 2015 Jul.
Article in English | MEDLINE | ID: mdl-26026993

ABSTRACT

The present debate on chemicals with Hormonal activity, often termed 'endocrine disruptors', is highly controversial and includes challenges of the present paradigms used in toxicology and in hazard identification and risk characterization. In our opinion, chemicals with hormonal activity can be subjected to the well-evaluated health risk characterization approach used for many years including adverse outcome pathways. Many of the points arguing for a specific approach for risk characterization of chemicals with hormonal activity are based on highly speculative conclusions. These conclusions are not well supported when evaluating the available information.


Subject(s)
Endocrine Disruptors/pharmacology , Endocrine System/drug effects , Endocrine Disruptors/toxicity , Humans , Toxicity Tests
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