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Relationship: 2767
Title
Cell injury/death leads to Decrease, Growth
Upstream event
Downstream event
Key Event Relationship Overview
AOPs Referencing Relationship
Taxonomic Applicability
Sex Applicability
| Sex | Evidence |
|---|---|
| Unspecific | Moderate |
Life Stage Applicability
| Term | Evidence |
|---|---|
| All life stages | Moderate |
Key Event Relationship Description
This KER describes the causal and predictive relationship whereby an increase in cell injury and/or cell death leads to a decrease in growth. The upstream KE, cell injury/death, represents loss of cellular viability or severe cellular damage resulting in apoptosis, necrosis, or other forms of lethal cellular injury. The downstream KE, decreased growth, represents reduced accumulation of biomass, body size, length, cell density, tissue mass, or other growth-related endpoints at organ, organism, or population levels. The biological logic of the KER is that growth requires a positive balance between production of new cellular material and loss of existing cells. When cell injury/death is sufficiently frequent, persistent, or spatially distributed across growth-relevant tissues, net cell accumulation is reduced and tissue or organismal growth is impaired. In unicellular systems, increased cell death directly reduces viable cell density and biomass accumulation. In multicellular organisms, the relationship depends on the affected tissue, the ability to compensate through proliferation or regeneration, and the timing of injury relative to developmental or growth windows.
This relationship is not intended to imply that all decreases in growth are caused by cell death. Growth can also decrease through reduced cell proliferation, altered energy allocation, endocrine disruption, nutrient limitation, or developmental delay without overt lethality. Rather, the KER applies when increased cell injury/death is of sufficient magnitude or duration to reduce the viable cellular pool needed for growth or to damage growth-relevant tissues. Within the ROS-growth AOP network, this KER provides a terminal convergence relationship for pathways in which oxidative stress, DNA strand breaks, or ATP depletion produce cytotoxicity that contributes to reduced growth.
Evidence Collection Strategy
Evidence for this KER was assembled using the same AI-human hybrid strategy applied across the ROS-growth AOP network. Initial evidence identification used AOP-Wiki relationship and key event mapping, prior ROS-growth concordance tables, and targeted literature searches. Search terms combined upstream and downstream concepts such as “cell death”, “cell injury”, “cytotoxicity”, “apoptosis”, “necrosis”, “viability”, “growth inhibition”, “growth retardation”, “developmental delay”, “biomass”, “cell density”, “condition index”, and “organism growth”, together with taxa and stressor terms including algae, Daphnia, copepod, bivalve, fish embryo, mammalian embryo, paraquat, cadmium, methanol, rotenone, gamma radiation, and oxidative stress. AOP-Wiki was consulted to confirm that Relationship 2767 links Event 55 to Event 1521 and to identify related AOP reuse contexts.
Candidate studies were prioritized when they measured both cell injury/death and a growth-related outcome in the same biological system, reported dose or concentration and exposure duration, or provided information relevant to temporal, dose-response, or incidence concordance. Large language model assistance was used only as an auxiliary screening and structuring tool to extract study metadata, identify potentially relevant endpoints, and prioritize records for expert review. Final inclusion decisions, interpretation of endpoints, and weight-of-evidence judgments were made by manual expert curation against the original article text. Mechanistic reviews were used to support biological plausibility, while primary experimental studies were used preferentially to support empirical concordance.
Evidence Supporting this KER
Biological Plausibility
Overall call: High. Growth at the level of a tissue, organ, organism, or cell population depends on net accumulation of cells and cellular biomass. Increased cell death directly lowers the number of viable cells and can reduce tissue mass, disrupt morphogenesis, or impair the capacity for biomass accumulation. This relationship is strongly supported by developmental and cell-size control principles showing that final tissue and organism size depend on the balance among cell growth, cell division, and cell death (Conlon and Raff, 1999). In embryos and developing organisms, excessive cell death can reduce cell number available for organ formation and growth, whereas in unicellular populations and cell cultures, cytotoxicity directly reduces viable cell density. The KER is therefore mechanistically plausible across taxa, although the magnitude of growth impairment depends on the tissue affected, compensatory proliferation, regeneration, and exposure duration.
Empirical Evidence
Overall call: Moderate. Empirical support is moderate because multiple studies report concordance between cell injury/death and growth-related effects, but the evidence is heterogeneous and not always designed specifically to test this KER. In several systems, cell injury/death and growth inhibition are measured at different time points, and growth can be affected by mechanisms other than cell death. Nevertheless, the available data support the expected direction of effect across algae, fish embryos, mollusks, and mammalian embryo models.
|
Biological system |
Stressor / context |
Upstream evidence: cell injury/death |
Downstream evidence: decreased growth |
Concordance interpretation |
Reference |
|
Chlamydomonas reinhardtii |
Paraquat |
Loss of membrane integrity measured by SYTOX Green; cell death observed at approximately 0.5 uM after 24 h. |
Reduced cell density/growth after 72 h; growth LOEC approximately 0.1 uM and EC50 approximately 0.26 uM. |
Partial temporal and endpoint concordance. Growth effects occurred at or below cytotoxicity thresholds, indicating that cell death contributes but is not the only driver of growth inhibition. |
Jamers and De Coen, 2010 |
|
Chlamydomonas reinhardtii |
Paraquat and herbicides |
SYTOX Green cell death observed with paraquat; cell injury occurred alongside ATP depletion and other stress endpoints. |
Assay system reported reduced growth/cell density and multiple mechanistic endpoints following herbicide exposure. |
Supports association between cytotoxicity and reduced population growth, but includes multiple parallel mechanisms. |
Nestler et al., 2012 |
|
Mouse and rat whole-embryo culture |
Methanol |
Cell death markedly elevated in embryos at growth-relevant concentrations. |
Mouse and rat embryo growth reduction observed in exposed cultures. |
Supports developmental concordance between increased embryonic cell death and growth impairment, with species differences in sensitivity. |
Abbott et al., 1995 |
|
Eastern oyster, Crassostrea virginica |
Cadmium and temperature interaction |
Hemocyte mortality, lysosomal destabilization, and cellular energy disruption observed under cadmium stress. |
Reduced condition index and increased mortality under combined cadmium and elevated temperature. |
Supports linkage between cellular injury and reduced growth/condition, although growth is modified by temperature and energy budget effects. |
Sokolova et al., 2005; Cherkasov et al., 2006 |
|
Fish embryos and juveniles |
Rotenone |
Histological lesions and tissue injury observed at low concentrations. |
Developmental delay and growth-related impairment reported after short-term exposure. |
Supports association between cellular/tissue injury and developmental growth impairment; direct measurement of cell death was limited. |
Melo et al., 2015 |
|
Marine copepod, Paracyclopina nana |
Gamma radiation |
Radiation induced oxidative stress and impaired survival/development. |
Growth retardation and failure of nauplii to develop to adults observed. |
Supports an adverse sequence from stress-induced cellular injury to growth retardation, although cell death was not always measured directly. |
Won and Lee, 2014 |
Uncertainties and Inconsistencies
The main uncertainty is that decreased growth is an integrative endpoint and can arise through several mechanisms that do not require overt cell death. Reduced proliferation, ATP depletion, endocrine disruption, altered energy allocation, nutrient limitation, delayed development, or behavioral effects can all reduce growth. For this reason, cell injury/death should be interpreted as a sufficient but not always necessary contributor to decreased growth. A second uncertainty is that many studies measure cytotoxicity and growth at different times or in different tissues, which limits direct evaluation of temporal concordance. In some algal studies, growth inhibition occurs at lower concentrations than overt cell death, suggesting that non-lethal impairment of proliferation, photosynthesis, or energy metabolism may precede cell death. Conversely, mild or localized cell injury may be compensated by repair or proliferation and may not lead to measurable growth reduction. These uncertainties support a moderate, rather than high, empirical call for this KER.
Known modulating factors
|
Modulating factor |
Relevant details |
Effect on the KER |
Supporting references |
|
Developmental stage |
Embryonic and larval stages, rapid growth phases |
Increases sensitivity because rapid tissue growth requires high net cell accumulation; cell death during development can disproportionately impair growth. |
Abbott et al., 1995; Conlon and Raff, 1999 |
|
Tissue regenerative capacity |
Capacity for compensatory proliferation or tissue repair |
Reduces probability that cell death will translate into growth impairment when surviving cells can replace lost cells. |
Conlon and Raff, 1999 |
|
Exposure duration and timing |
Acute versus chronic exposures; timing relative to growth window |
Longer or developmentally timed exposures increase probability of growth effects from cell loss. |
Jamers and De Coen, 2010; Melo et al., 2015 |
|
Energy and nutritional status |
Energy budget, food availability, metabolic reserve |
Can increase or decrease impact of cell death on growth by altering compensatory capacity and resource allocation. |
Sokolova, 2013; Cherkasov et al., 2006 |
|
Environmental stressors |
Temperature, oxygen availability, salinity, co-exposures |
Can amplify cytotoxicity or reduce compensatory growth responses, modifying downstream growth effects. |
Cherkasov et al., 2006; Won and Lee, 2014 |
Quantitative Understanding of the Linkage
Overall call: Low to moderate. Quantitative understanding is limited because the relationship between cell injury/death and growth depends on the proportion of cells affected, tissue location, developmental timing, compensatory proliferation, regenerative capacity, and organismal energy allocation. At a conceptual level, the linkage is quantitative: growth rate reflects the balance between biomass accumulation and biomass or cell loss, so increasing the frequency or magnitude of cell death should reduce net growth if cell replacement or compensatory growth is insufficient. However, few studies provide response-response models that predict growth reduction from a measured degree of cell injury/death across taxa or stressors.
Response-response Relationship
In cell populations and unicellular organisms, the quantitative relationship can be relatively direct because viable cell density is part of the growth measurement. In multicellular organisms, the relationship is less direct because growth can continue despite localized cell death if compensatory proliferation or tissue repair occurs. Some data show concordance between cytotoxicity and growth inhibition, but these data are generally insufficient to define universal thresholds. Therefore, quantitative understanding should be considered low to moderate for broad AOP-Wiki application, with higher confidence possible for specific model systems where cell viability and growth rate are measured in the same assay and time course.
Time-scale
Known Feedforward/Feedback loops influencing this KER
Domain of Applicability
The KER is applicable to biological systems in which growth depends on maintenance or expansion of viable cell number or biomass. This includes unicellular populations, developing embryos, juvenile organisms, growing tissues, and adult organisms in which tissue condition or somatic growth is assessed. Taxonomic applicability is broad across eukaryotes, but empirical support is strongest for algae, aquatic invertebrates, mollusks, fish, and mammalian embryo or cell models. The KER is not sex-specific, but sex, endocrine status, life stage, and environmental context may modulate sensitivity. The relationship is most relevant when cell injury/death is sufficiently extensive, sustained, or located in growth-relevant tissues. It is less predictive when growth is reduced by upstream mechanisms that suppress proliferation or metabolism without substantial cell death.
References
Abbott, B. D., Harris, M. W., & Birnbaum, L. S. (1995). Cell death in rat and mouse embryos exposed to methanol in whole embryo culture: Evaluation of the role of the p53 tumor suppressor gene. Teratogenesis, Carcinogenesis, and Mutagenesis, 15(3), 147–169.
Cherkasov, A. S., Biswas, P. K., Ridings, D. M., Ringwood, A. H., & Sokolova, I. M. (2006). Effects of acclimation temperature and cadmium exposure on cellular energy budgets in the marine mollusk Crassostrea virginica: Linking cellular and mitochondrial responses. Journal of Experimental Biology, 209(7), 1274–1284.
Conlon, I., & Raff, M. (1999). Size control in animal development. Cell, 96(2), 235–244.
Jamers, A., & De Coen, W. (2010). Effect assessment of the herbicide paraquat on a green alga using differential gene expression and biochemical biomarkers. Environmental Toxicology and Chemistry, 29(4), 893–901.
Knops, M., Altenburger, R., & Segner, H. (2001). Alterations of physiological energetics, growth and reproduction of Daphnia magna under toxicant stress. Aquatic Toxicology, 53(2), 79–90.
Melo, K. M., Oliveira, R., Grisolia, C. K., Domingues, I., Pieczarka, J. C., de Souza Filho, J., & Nagamachi, C. Y. (2015). Short-term exposure to low doses of rotenone induces developmental, biochemical, behavioral, and histological changes in fish. Environmental Science and Pollution Research, 22(18), 13926–13938.
Nestler, H., Groh, K. J., Schönenberger, R., Eggen, R. I. L., & Suter, M. J.-F. (2012). Multiple-endpoint assay provides a detailed mechanistic view of responses to herbicide exposure in Chlamydomonas reinhardtii. Aquatic Toxicology, 110–111, 214–224.
Organisation for Economic Co-operation and Development (OECD). (2018). Users’ handbook supplement to the guidance document for developing and assessing adverse outcome pathways. OECD Series on Adverse Outcome Pathways No. 1. OECD Publishing, Paris.
Organisation for Economic Co-operation and Development (OECD). (2021). Guidance document for the scientific review of adverse outcome pathways. OECD Series on Testing and Assessment No. 344. OECD Publishing, Paris.
Sokolova, I. M. (2013). Energy-limited tolerance to stress as a conceptual framework to integrate the effects of multiple stressors. Integrative and Comparative Biology, 53(4), 597–608.
Sokolova, I. M., Sokolov, E. P., & Ponnappa, K. M. (2005). Cadmium exposure affects mitochondrial bioenergetics and gene expression of key mitochondrial proteins in the eastern oyster Crassostrea virginica Gmelin (Bivalvia: Ostreidae). Aquatic Toxicology, 73(3), 242–255.
Won, E. J., & Lee, J. S. (2014). Gamma radiation induces growth retardation, impaired egg production, and oxidative stress in the marine copepod Paracyclopina nana. Aquatic Toxicology, 150, 17–26.