Authors: Qiang Wang, Håvard Jostein Haugen, Dirk Linke, Ståle Petter Lyngstadaas, Qianli Ma
Categories: Article, chemical debridement agents, residuals, cytocompatibility, regeneration, apoptosis
Source: ACS Biomaterials Science & Engineering
of Chemical Cleaning Agents Impair Peri-Implant Cell Viability: An in Vitro Study
Authors: Qiang Wang, Håvard Jostein Haugen, Dirk Linke, Ståle Petter Lyngstadaas, Qianli Ma
Background: Chemical
debridement agents are commonly
used during
the cleaning of implants for peri-implantitis treatment; however,
how these agents affect lesion healing remains unclear. In addition,
the dose- and time-dependent effects of these residuals on implant
biocompatibility remain poorly understood. Materials and
We evaluated the effects of active compounds in commercial products-3%
hydrogen peroxide (H2O2), 0.43% sodium hypochlorite
(NaClO), and 0.12% chlorhexidine with 0.05% cetylpyridinium chloride
(CHX-CPC) at graded dilutions on murine osteoblastic cells (MC3T3-E1),
human gingival fibroblasts (HGFs), and human bone marrow mesenchymal
stromal cells (hBMSCs). Cells were cultured for 24 h, then exposed
to the agents for 2, 12, or 24 h. Cytotoxicity and viability were
assessed using lactate dehydrogenase (LDH) release and CCK-8 assays,
while cell morphology was examined by scanning electron microscopy
(SEM). Apoptotic gene expression (BCL2, MCL1, BAX) was analyzed after 2 h using quantitative
PCR. Results: At high concentrations, H2O2 and
NaClO significantly reduced LDH activity in supernatant, likely due
to oxidant-induced enzyme inactivation. All three agents inhibited
cell viability in a dose- and time-dependent manner, accompanied by
cell shrinkage and deformation. Among the tested cell types, hBMSCs
displayed greater resistance to H2O2, maintaining
proliferative viability at 0.15% (1:20 dilution). Gene expression
analysis revealed that concentrated H2O2 and
CHX-CPC downregulated BCL2 and MCL1 expression in MC3T3-E1 cells, with broader suppression of these
genes observed in HGFs across all agents. In hBMSCs, high concentrations
of the agents did not significantly reduce BCL2 and MCL1 levels. Conclusion: Residual chemical debridement agents,
when inadequately removed, compromise the viability of cells in peri-implant
tissues in a dose- and time-dependent manner. hBMSCs exhibited greater
resistance to apoptosis than MC3T3-E1 cells and HGFs. Thorough removal
of residual chemical cleaning agents after peri-implant debridement
is therefore crucial to preserve the biocompatibility of the implant
and the healing potential of peri-implant tissues.
The long-term success
of dental implants depends not only on stable
primary osseointegration but also on robust, stable, and long-lasting
soft-tissue integration at the transgingival region. This soft-tissue
integration is hindered by the continuing growth of oral biofilms
on the implant surface, which can trigger chronic inflammatory responses. Accordingly, sustained peri-implant health requires
both periodical disruption of the microbial biofilm to prevent pathogenic
colonization and reliable achievement of osseointegration and soft-tissue
integration after surgery. Numerous nonsurgical
debridement strategies have been proposed to eliminate biofilms from
implant surfaces, yet no consensus has been reached regarding the
superiority of any single method.
,
Among these
approaches, chemical agents such as chlorhexidine (CHX), citric acid,
sodium hypochlorite (NaClO), and H2O2 are widely
employed for implant surface decontamination. While these agents are
effective in killing bacteria and/or removing biofilm, their biological
effects on cells in peri-implant tissues remain incompletely understood.
,
In our previous work, we investigated the cytocompatibility
of
commonly used chemical debridement agents on titanium implant surfaces,
including H2O2, Poloxamer, Perisolv (0.43% NaClO),
and Paroex (0.12% CHX +0.05% cetylpyridinium chloride, CPC). Peri-implant
tissues comprise diverse cell populations, including immune, mesenchymal,
epithelial, and fibroblast lineages. To
represent the key cellular compartments essential for peri-implant
regeneration, we selected human bone marrow mesenchymal stem cells
(hBMSCs), as progenitors of osteoblasts that are critical for osseointegration, and human gingival fibroblasts (HGFs), the main
cellular component of peri-implant connective tissue that forms the
protective soft-tissue seal at the transmucosal region. In addition, we included the murine preosteoblastic
MC3T3-E1 cells, which exhibit proliferative and mineralization behaviors
comparable to those of human primary osteoblasts. Our findings revealed that the adhesion and proliferation
of hBMSCs were significantly impaired on commercial titanium implant
surfaces (OsseoSpeed) after treatment with 3% H2O2 and commercial formulations such as Perisolv (0.43% NaClO) and Paroex
(0.12% CHX +0.05% CPC). Moreover, oxidant-based agents (H2O2 and NaClO) suppressed key genes associated with proliferation,
antiapoptosis, and cellular attachment to titanium. These results highlight the potential adverse cellular
effects of chemical cleaning procedures and emphasize the importance
of adequate post-treatment rinsing to minimize residual toxicity.
Although residues of chemical debridement agents can persist around
implants after treatment, the dose- and
time-dependent effects of these agents on peri-implant tissue regeneration
remain incompletely elucidated. To address this knowledge gap, we
systematically evaluated and analyzed the biological impact of residual
active components from widely used debridement agents-H2O2, NaClO, and CHX-CPC on MC3T3-E1, HGFs, and hBMSCs to
inform safer protocols that minimize cytotoxicity and preserve a regenerative
peri-implant environment, thereby supporting the long-term success
of implant treatment. To simulate these clinical conditions in which
traces of these agents may remain in peri-implant pockets, test solutions
were prepared at graded dilutions (1:2000, 500, 200, 100, 50,
1:20, and 5) and applied to cells for 2, 12, or 24 h. Cytocompatibility
(cytotoxicity and proliferative viability) and apoptosis-related gene
expressions (BCL2, MCL1, BAX) were subsequently examined to characterize cellular
responses.
The debridement
chemicals used included hydrogen peroxide (H2O2; Cat. No 1.08597, Sigma-Aldrich, Germany), sodium hypochlorite (NaClO;
Cat. No 87939.29, VWR, Germany), chlorhexidine digluconate (CHX; aqueous
solution, Cat. No 41385.AC, VWR, Germany) and cetylpyridinium chlorite
(CPC, Cat. No ACRO226991000, VWR, Belgium). The concentrations of
the different debridement chemicals were selected based on those found
in the commercial products Perisolv (Regedent AG) and Gum Pareox (Sunstar).
Stock solutions were diluted in culture medium supplemented with 10%
FBS (fetal bovine serum, Cat. No. A5256701, Gibco, NY, USA) or platelet
lysate (PIPL, kindly donated by the Blood Bank, Landspitali University
Hospital, Reykjavik, Iceland) to obtain graded concentrations as shown
in Table
.
MC3T3-E1 cells (CRL-2593,
ATCC, Manassas, VA, USA) were cultured in Minimum Essential Medium
Alpha (α-MEM, A1049001, Gibco, USA) supplemented with 10% FBS
(FCS, 20170–106, Gibco, USA) and 1% penicillin–streptomycin
(Gibco, Grand Island, Cat. No 15070–063, NY, USA). HGFs (Passage7,
HFIB-G; Provitro, Berlin, Germany) were cultured in DMEM -low glucose
(DMEM; Merck, Cat. No D5546, Germany) with 10% FBS, 1% P/S, and 5
mM d-glucose. hBMSCs (Passage 6, Cat. No PT-2501, Lonza,
Switzerland) were cultured in DMEM/F12 with Glutamax (Gibco, Grand
Island, Cat. No 31331–093, NY, USA) with 10% PIPL, 1% P/S,
and 2 IU/ml heparin (LEO Pharma A/Sm Ballerup, Denmark). Cells were
incubated at 37 °C in a humidified incubator with 5% CO2. Ethical approval was not required for the study, in accordance
with local legislation and institutional requirements, because only
established, commercially available cells were used.
Assay
Cytotoxicity was assessed using the LDH Cytotoxicity Detection Kit (Sigma-Aldrich, Cat. No 11644793001). Cells were seeded in 96-well plates at a density of 7500 cells per well (≈2.3 × 10^4^ cells/cm^2^) and cultured for 24 h. The medium was then replaced with media containing diluted agents and incubated for an additional 2, 12, or 24 h. Supernatants were collected and LDH activity was quantified according to the manufacturer’s instructions. Absorbance was measured at 490 nm using a microplate reader.
Cell proliferative viability was measured using the Cell Counting Kit-8 (CCK-8; Abcam, ab228554). Cells were seeded in 96-well plates at a density of 7500 cells per well (≈2.3 × 10^4^ cells/cm^2^) and cultured for 24 h. The medium was then replaced with diluted agents and incubated for 2, 12, or 24 h. After treatment, the medium was replaced with fresh medium (10% FBS or PIPL) and incubated for an additional 4 h. Aliquots of 100 μL from each well were transferred to a new 96-well plate, and absorbance was measured at 460 nm using a microplate reader, which indirectly reflected cell proliferative activity.
Electron Microscopy (SEM)
Round coverslips (8 mm in diameter; MENZCB00080RA120, VWR, Germany) were placed in 24-well plates, and cells were seeded at a density of 2.5 × 10^4^ cells per well (≈1.3 × 10^4^ cells/cm^2^). After 24 h, the medium was replaced with diluted agents and incubated for 2, 12, or 24 h. Following treatment, cells were fixed overnight at 4 °C in a solution of 4% paraformaldehyde and 2% glutaraldehyde in HEPES buffer. After that, samples were washed in HEPES buffer, dehydrated through a graded ethanol (30%, 50%, 70%, 90%, twice in 100%, 5 min each round), and immersed in hexamethyldisilazane (HDMS; Sigma-Aldrich, Cat. No. 86944, Burghausen, Germany) for 8 h, allowing slow evaporation. After being sputter-coated with gold, the cell microstructures were examined under an SEM (TM-1000, Hitachi, Tokyo, Japan).
PCR (qPCR)
TaqMan qPCR probes were used to quantify gene expression. For human cells: β*-actin* (Hs01060665_g1), BCL2 (Hs00608023_m1), and BAX (Hs00180269_m1), and MCL1 (Hs01050896_m1). For mouse β*-actin* (Mm02619580_g1), BCL2 (Mm00477631_m1), BAX (Mm00432051_m1), and MCL1 (Mm01257351_g1) (all purchased from ThermoFisher, Cat. No 4331182). Amplification was performed using TaqMan Fast Advanced Master Mix (Thermofisher, Cat. No 4444556). qPCR was conducted on an AriaMx Real-time PCR System (Agilent, USA) in 10 μL reactions containing 3.5 μL PCR-grade water (Sigma-Aldrich, USA, Cat. No W4502), 0.5 μL probe, 5 μL probe mix, and 1 μL template DNA. Cycling conditions 50 °C for 2 min (predenaturation), 95 °C for 20 s (polymerase activation), followed by 40 cycles of 95 °C for 1 s (denaturation) and at 60 °C for 20 s (annealing).
Analysis
Unless otherwise noted, experiments were repeated thrice with at least three to four replicates per group. Data were analyzed using SPSS 28.0 (IBM, USA) and are presented as the mean ± standard deviation. Significant differences between groups were identified using one-way analysis of variance (ANOVA) followed by a Student–Newman–Keuls post hoc test for parametric data or Kruskal–Wallis tests followed by Dunn’s multiple comparison tests for nonparametric data. Differences were considered statistically significant when p < 0.05. The data were analyzed and plotted using Prism 10.4.0 (GraphPad Software, USA), with significant differences indicated by different letters (e.g., a, b, c), while groups sharing the same letter are not significantly different (e.g., ab vs b). Figures were formatted using Inkscape (version 1.3.2, Inkscape Project, https://inkscape.org/).
Chemicals on MC3T3-E1 Cells
H2O2 Treatment
SEM revealed that cells
under 0.0015%
H2O2 (1:2000 dilution) maintained normal morphology
with multidirectional intercellular connections. In contrast, aggravated
shrinkage was observed with H2O2 concentrations
ranging from 0.006% (1:500) to 0.6% (1:5). At 0.006% (1:500) and 0.015%
(1:200), cells exhibited irregular protrusions after 2 h of exposure,
which diminished and were accompanied by further shrinkage over time.
Reduced intercellular connections were observed at concentration of
0.015% (1:200). At 0.06% (1:50) and 0.15% (1:20), the cells became
smoother and more spherical. At 24 h, the morphology was no longer
maintained in most cells, with evident loss of normal cell shape and
integrity (Figure
A). The SEM morphology of the control group is shown in Figure S1. Proliferative viability was strongly
inhibited at concentrations ≥0.006% (1:500), reaching levels
comparable to the 1% Triton X-100 positive control (Figure
B). LDH activity in the supernatant
rose in a dose-dependent manner initially, from 0.0015% (1:2000) to
0.15% (1:20). Still, it showed marked reduction at 0.6% (1:5) after
2 h, from 0.15% (1:20) to 0.6% (1:5) after 12 h, and from 0.06% (1:50)
to 0.6% (1:5) after 24 h (Figure S2).

Under NaClO treatment, SEM showed aggravated shrinkage, increasing
from 0.00215% (1:200) to 0.086% (1:5), with the most pronounced changes
observed at 0.0215% (1:20) and 0.086% (1:5), where cells adopted a
spherical morphology. Shrinkage became more evident with prolonged
exposure, being more evident after 24 h than after 2 h, particularly
at 0.0215% (1:20) and 0.086% (1:5) (Figure
A). Unlike H2O2, which
markedly reduced proliferation at concentrations ≥0.006% (1:500),
NaClO preserved or even enhanced proliferation at 0.000215% (1:2000)
to 0.0086% (1:50). However, compromised viability emerged at higher
concentrations, at 0.086% (1:5) after 2 h, and from 0.0215% (1:20)
to 0.086% (1:5) after 12/24 h, reaching Triton-comparable levels (Figure
B). LDH activity
in the supernatant declined in a dose-dependent manner, most notably
at 0.086% (1:5) (Figure S2).

CHX-CPC induced progressive volume loss and cellular rounding, most evident at 0.006% CHX +0.0025% CPC (1:20). In contrast, at 0.024% CHX +0.01% CPC (1:5), most cells exhibited disrupted membranes and micropore formation across all time points. Even at 0.00006% CHX +0.000025% CPC (1:2000) and 0.00024% CHX +0.0001% (1:500), prolonged exposure intensified shrinkage, with cells volume being smaller at 24 h compared to 2 h (Figure A). Proliferative viability was maintained or enhanced at 0.00006% CHX +0.000025% CPC (1:2000) to 0.0024% CHX +0.001% (1:50) at 2 h, 0.00006% CHX +0.000025% CPC (1:2000) to 0.0012% CHX +0.0005% (1:100) at 12 h, and 0.00006% CHX +0.000025% CPC (1:2000) to 0.0006% CHX +0.00025% (1:200) at 24 h, but significantly declined at higher concentrations. Viability was also time-dependent: for example, CHX-CPC at 0.0024% CHX +0.001% (1:50) had no effect at 2 h but reduced viability at 12 h. In comparison, 0.0012% CHX +0.0005% (1:100) was nontoxic at 12 h, but cytotoxic at 24 h (Figure B). LDH activity reached Triton-equivalent levels at 0.024% CHX +0.01% CPC (1:5) after 2 h, peaked at 0.0024% CHX +0.001% (1:50) to 0.024% CHX +0.01% CPC (1:5) after 12/24 h (Figure S2).

HGFs
Similar to MC3T3-E1 cells, SEM showed progressively increased (dose-dependent) cell shrinkage and reduced intercellular connections at higher concentrations across all time points. For instance, at 2 h, shrinkage was enhanced at higher concentrations, peaking at 0.6% (1:5), at which point cells lost their normal morphology and detached from neighboring cells. With prolonged exposure, even at 0.006% (1:500) and 0.015% (1:200), shrinkage intensified, irregular protrusions disappeared, leaving cells more spherical at 12 and 24h when compared to 2 h (Figure A). Similar to MC3T3-E1 cells, proliferative viability of HGFs was strongly inhibited at concentrations ≥0.006% (1:500), comparable to Triton (Figure B). LDH activity increased at low concentrations. Still, it declined at 0.6% (1:5) at 2h, from 0.06% (1:50) to 0.6% (1:5) at 12 h, from 0.03% (1:100) to 0.6% (1:5) at 24 h (Figure S2).

NaClO induced dose-dependent shrinkage in HGFs, most severe at 0.086% (1:5), where cells lost intercellular contacts and basic morphology (Figure A). Viability was markedly compromised at concentrations ≥0.0086% (1:50). Notably, HGFs were more sensitive to NaClO than MC3T3-E1 cells, as 0.0086% (1:50) NaClO impaired HGF proliferation but had no effect on MC3T3-E1 (Figure B). LDH activity decreased significantly from 0.0043% (1:100) to 0.086% (1:5) at 2 h; from 0.0086% (1:50) to 0.086% (1:5) at 12 h; and from 0.0043% (1:100) to 0.086% (1:5) at 24 h (Figure S2).

Under CHX-CPC, HGFs morphology changed in both a dose- and time-dependent manner. Shrinkage and reduced intercellular interactions were more pronounced at concentrations ≥0.0012% CHX +0.0005% CPC (1:100), especially at 0.024% CHX +0.01% CPC (1:5). At 0.0012% CHX +0.0005% CPC (1:100), cell volume loss intensified with lmore prolongedexposure, particularly at 24 h (Figure A). Similar to MC3T3-E1 cells, CHX-CPC inhibited HGFs proliferative viability at concentrations ≥0.006% CHX +0.0025% CPC (1:20) after 2 h; ≥0.0024% CHX +0.001% CPC (1:50) after 12 h; and ≥0.0006% CHX +0.00025% CPC (1:200) after 24 h (Figure B). LDH activity increased significantly from 0.006% CHX +0.0025% CPC (1:20) to 0.024% CHX +0.01% CPC (1:5) at 2 h; from 0.0024% CHX +0.001% CPC (1:50) to 0.024% CHX +0.01% CPC (1:5) at 12 and 24 h (Figure S2).

hBMSCs
In hBMSCs, H2O2 induced dose-dependent shrinkage,
most evident at 0.6% (1:5). At 0.06% (1:50), the cell membranes ruffled.
At 0.15% (1:20), the nuclei were visible at 2 h. Still, they disappeared
with longer exposure (12 and 24 h) (Figure
A). Unlike MC3T3-E1 and HGFs, hBMSCs maintained
viability at control levels from 0.0015% (1:2000) to 0.15% (1:20),
with inhibition only observed at 0.6% (1:5), reaching Triton-equivalent
levels (Figure
B).
LDH activity in supernatant rose initially. Still, it declined at
0.6% (1:5) (Figure S2).

under NaClO Treatment
NaClO induced cell shrinkage in hBMSCs at 0.0086% (1:50), with worsening at higher concentrations. At 0.0086% (1:50), morphology was partially maintained with some protrusions. Still, at 0.0215% (1:20) and 0.086% (1:5), cell shrank severely and lost intercellular contacts (Figure A). Viability inhibition was not only dose-dependent: proliferative viability compromised when concentration ≥0.0215% (1:20) after 2 h, and concentrations ≥0.0086% (1:50) after 12/24 h, but also time-dependent: no inhibition was observed at 0.0086% (1:50) after 2 h, but significant reduction occurred after 12 and 24 h (Figure B). Similar to the other two cell types, NaClO maintained control-comparable LDH activity at low concentrations but declined significantly when concentrations ≥0.0086% (1:50) (Figure S2).

CHX-CPC induced shrinkage and micropore formation in hBMSCs at 0.006% CHX +0.0025% (1:20) and 0.024% CHX +0.01% CPC (1:5) across all time points. At 0.024% CHX +0.01% CPC (1:5), cell membranes were disrupted, and cells lost their normal morphology. Even at 0.0012% CHX +0.0005% CPC (1:100) and 0.0024% CHX +0.001% CPC (1:50), membrane ruffling and shrinkage became more evident with more prolonged exposure (12 and 24 h) (Figure A). Proliferative viability followed the same dose- and time-dependent pattern as the other two cell inhibition appeared from 0.006% CHX +0.0025% (1:20) to 0.024% CHX +0.01% CPC (1:5) after 2h; from 0.0024% CHX +0.001% CPC (1:50) to 0.024% CHX +0.01% CPC (1:5) after 12 h; and from 0.0012% CHX +0.0005% CPC (1:100) to 0.024% CHX +0.01% CPC (1:5) after 24 h (Figure B). The highest concentrations of CHX-CPC yielded LDH activity comparable to Triton, specifically, 0.024% CHX +0.01% CPC (1:5) at 2 h; from 0.006% CHX +0.0025% (1:20) to 0.024% CHX +0.01% CPC (1:5) at 12 h; and from 0.0024% CHX +0.001% CPC (1:50) to 0.024% CHX +0.01% CPC (1:5) at 24 h (Figure S2).

In
MC3T3-E1 cells, BCL2 increased at 0.0015% (1:2000)
to 0.015% (1:200) but returned to control-level at 0.03% (1:100). MCL1 was elevated at 0.0015% (1:2000) and decreased under
higher concentrations, with BAX significantly upregulated
when concentrations ≥0.006% (1:500) (Figure
C). HGFs showed a similar pattern, with
elevated BCL2 and MCL1 at 0.0015%
(1:2000) but reduced at higher concentrations. In contrast, BAX increased significantly (Figure
F). In hBMSCs, BCL2 was
reduced from 0.0015% (1:2000) to 0.006% (1:500), but restored under
0.015% (1:200) and 0.03% (1:100) of H2O2. MCL1 was unchanged at 0.0015% (1:2000), increased from 0.006%
(1:500) to 0.015% (1:200), and returned to baseline at 0.03% (1:100). BAX was significantly upregulated compared with the control
(Figure
I).

In MC3T3-E1 cells, BCL2 decreased overall, with a modest rise at high concentrations. MCL1 decreased at 0.0043% (1:100) but peaked at 0.0086% (1:50), while BAX remained comparable to control (Figure D). HGFs showed increased BCL2 at 0.000215% (1:2000). Still, they declined toward control-levels at 0.00215% (1:200). MCL1 was reduced only at 0.0215% (1:20), with BAX significantly upregulated at 0.0215% (1:20) (Figure G). In hBMSCs, both BCL2 and MCL1 peaked at 0.0215% (1:20), while BAX was significantly reduced from 0.000215% (1:2000) to 0.0086% (1:50), and restored at 0.0215% (1:20) (Figure J).
In MC3T3-E1 cells and HGFs, BCL2 and MCL1 rose at low concentrations but dropped sharply at 0.006% CHX +0.0025% CPC (1:20) (Figure E,H). In hBMSCs, BCL2 was reduced from 0.0012% CHX +0.0005% CPC (1:100) to 0.006% CHX +0.0025% CPC (1:20), while MCL1 was strongly upregulated at the highest concentration (dilution of 20) (Figure K). Under 0.0024% CHX +0.001% CPC (1:50) and 0.006% CHX +0.0025% CPC (1:20), BAX was unchanged in MC3T3-E1 cells and HGFs, while suppressed in hBMSCs (Figure E–K).
Our previous study, using
a titanium coin model, showed that chemical
compounds present in commercial debridement agents, even after vigorous
saline flushing, impaired cell attachment and proliferation in peri-implant
tissue. H2O2, Perisolv, and Paroex were particularly
cytotoxic to hBMSCs, and transcriptional analysis after 2 h of exposure
revealed suppression of genes regulating proliferation, adhesion,
and antiapoptosis. A key limitation of
this earlier study, however, was the inability to quantify residual
concentrations, leaving uncertainty about how dose and exposure time
influence biocompatibility. To address this, we systematically exposed
MC3T3-E1, HGFs, and hBMSCs to different concentrations of H2O2, NaClO, and CHX-CPC for 2, 12, and 24 h. The 2 h time
point was selected for qPCR to confirm transcriptional changes observed
in our earlier work.
All three chemical components reduced viability
in a clear dose-
and time-dependent fashion. Functionally, hBMSCs were more tolerant
only to H2O2, whereas their viability in response
to NaClO and CHX-CPC was similar to that of MC3T3-E1 cells and HGFs.
Although no previous study has directly compared the cytotoxicity
of H2O2 across MC3T3-E1, HGFs, and hBMSCs under
identical conditions, threshold values for each cell type have been
reported individually. For MC3T3-E1 cells, Dandan et al. demonstrated
that 2h exposure to 600 μM H2O2 (0.002%)
markedly reduced cell viability in vitro. Another study reported that 24 h exposure to 500 μM H2O2 (0.0017%) similarly impaired MC3T3-E1 viability. In our study, 0.0015% H2O2 (441 μM; 2000 dilution) did not exert cytotoxic effects
on MC3T3-E1 cells, whereas 0.006% H2O2 (1760
μM; 500 dilution) significantly reduced viability, consistent
with previously reported cytotoxic thresholds. For HGFs, prior research
indicated that even ≤0.0015% H2O2 (441
μM) for 1 h significantly decreased survival, suggesting a higher sensitivity than we observed, as 2–24
h exposures at the same concentration (441 μM; 2000 dilution)
did not reduce HGFs viability in our experiment. For hBMSCs, viability
was reported to decline significantly after 8 h at ≥ 200 μM
H2O2 (0.00068%; ∼49% survival), and even 2 h at 125 μM (0.000425%) reduced
viability by ∼42%, indicating
lower toxic thresholds than those observed in our data. These discrepancies,
particularly the relatively higher tolerance of HGFs and hBMSCs in
our study, are likely attributable to differences in exposure duration,
donor source, and passage number.
SEM showed canonical apoptotic morphology that intensified with higher
Cell shrinkage, rounding with surface smoothing, membrane ruffling, and fragmentation into small bodies; these features match the classic description of apoptosis. , Notably, at 2 h, hBMSCs showed a stronger antiapoptotic transcriptional response, maintaining or upregulating BCL2 and MCL1 at high concentrations, despite having a morphology comparable to the other cell types at matched doses, suggesting gene-level buffering that may precede overt structural rescue.
Interestingly, LDH
readout declined at the highest concentrations
of H2O2 and NaClO. This does not indicate reduced
cytotoxicity; it most likely reflects assay interference, because
LDH is unstable under oxidative conditions. Kendig et al. demonstrated
that reactive oxidants directly inactivate LDH in culture medium,
and that LDH is particularly susceptible to degradation under oxidative
conditions, as cellular glutathione is insufficient to protect this
enzyme, leading to an artifactual fall in measured activity despite
ongoing membrane damage. Accordingly,
the LDH assay is not suitable as a stand-alone cytotoxicity test in
the presence of oxidant-based reagents. It can yield false-negative
(or inversely dose-dependent) results, especially at high concentrations.
The cytotoxicity of H2O2 has been extensively
reported. Gingival fibroblasts exhibit profound sensitivity, with
100 μmol/L H2O2 (∼0.03%) reducing
proliferation by 80%, and even lower
concentrations (0.00068–0.0010%) impair stemness in rat BMSCs. In vivo (mouse) rinsing with 0.75–1.5%
H2O2, 4×/day for 2 weeks, occasionally
developed erythema and mucosal irritation in healthy volunteers. This aligns with Abedi et al., who noted that
excessive ROS production may hinder tissue repair, as it often causes
severe tissue injury and cell damage. Our results align with these findings, demonstrating that H2O2 reduces viability and antiapoptotic responses
across various cell types in peri-implant tissues. However, it was
reported that plaque and salivary bacteria rapidly degrade H2O2 in vitro, with complete removal of up to ∼300
mmol/L (∼1%) within 15 min This
may explain why low-concentration H2O2 in dentifrices
(0.75%) is generally safe for oral hard and soft tissues, with reported
benefits in plaque control and wound healing. Hence, while our in vitro data confirm cytotoxic potential, the
clinical relevance requires validation in clinical settings. Variations
in bacterial species and numbers around dental implants may significantly
affect the potential for H2O2 consumption, making
it difficult to determine the exact “safe dose” for
H2O2 application. It may differ significantly
for patients with varying oral hygiene and genetic backgrounds.
,
NaClO, a potent oxidizing and proteolytic agent, is widely used for root canal irrigation due to its capacity to dissolve necrotic tissue and disrupt biofilms. Its cytotoxicity arises from reactive species such as OCl^–^, HOCl, and OH-, which elevate pH, while HClO also directly interacts with DNA bases, resulting in oxidative damage and, eventually, cell death. −
Although complications may occur with the inadvertent extrusion of concentrated NaClO, its clinical use persists due to superior antimicrobial activity. In vitro, NaClO reduces hBMSC viability in a concentration- and time-dependent manner, with significant inhibition at 0.05% after 2 h, which is similar to our findings that proliferative viability was significantly inhibited even at 0.02% for 2 h (1:20 dilution of NaClO). These results highlight the need for cautious clinical application and further in vivo evaluation.
CHX, a cationic diphenyl compound with broad-spectrum bactericidal activity, is widely used in periodontal and peri-implant therapy. Its cytotoxicity, however, is well documented. Gisele et al. showed that CHX induces endoplasmic reticulum stress, leading to apoptosis or necrosis. Low concentrations (0.000125% and 0.001%) slightly increased BCL2 in murine fibroblasts, whereas ≥0.004% caused necrotic death due to membrane disruption. M. Giannell et al. further demonstrated dose- and time-dependent cytotoxicity in gingival fibroblasts and alveolar osteoblasts, mediated by mitochondrial dysfunction, intracellular Ca^2+^ overload, and oxidative stress, cautioning against its direct use in regenerative procedures. Goldschmidt et al. reported that even brief exposure (10 min) to 0.004% CHX impaired protein synthesis, while James et al. confirmed significant toxicity on human fibroblasts, myoblasts, and osteoblasts at concentrations up to 100-fold below the clinical use level (2%). And Marzena et al. showed that 0.002% CHX for 15 min did not impair HGFs proliferation or morphology, but ≥0.04% markedly reduced viability. Although the exposure time and dilution medium differ (CHX is diluted in FBS-free solutions), consistent with these findings, our results confirmed dose-dependent cytotoxicity of CHX-CPC, underscoring the potential risk of impaired osseointegration and soft tissue healing if residual CHX persists.
CPC is a quaternary ammonium compound with amphiphilic properties and broad-spectrum antimicrobial activity, widely used in dentistry, particularly in mouthwashes alone or in combination with CHX, and generally associated with fewer side effects than CHX. , In vitro studies simulating clinical use have reported limited cytotoxicity. For instance, Geneviève et al. showed that 1 min exposure to 0.05% CPC with 0.2% NaF (1/4 dilution) did not significantly affect epithelial cell viability, and Heitor et al. found no significant toxicity in L929 murine fibroblasts after 48 h exposure to 0.0195% CPC. By contrast, Doris et al. reported cytotoxicity in retinal pigment epithelial cells and keratinocytes at micromolar concentrations (150-fold lower than 0.05%), although this involved 48 h exposure, well beyond clinically relevant conditions. Similarly, Mustafa et. al showed that 2 min exposure to various dilutions of commercial mouthwashes (Colgate Plax, Oral B Proexpert) reduced fibroblast viability; however, these products contain additional components (e.g., sorbitol, poloxamer 407, propylene glycol, sodium fluoride, sodium saccharin, etc.), and the use of murine fibroblasts limits direct clinical interpretation. Consequently, we assume that the cytotoxicity of CHX-CPC is primarily derived from CHX in the present study.
Our previous work demonstrated that oxidant-based agents (H2O2, NaClO) activate the intrinsic apoptotic pathway, a process regulated by the BCL-2 family of proteins.
In this system, pro-survival proteins such as BCL-2 and MCL1 oppose
pro-apoptotic proteins such as BAX and BAK. Apoptosis occurs when the balance shifts, allowing BAX and BAK to oligomerize and form macro-pores in
the mitochondrial outer membrane, thereby permeabilizing the mitochondrial
outer membrane (MOMP) and triggering caspase activation. Since MOMP
is the critical step at which a cell irreversibly commits to undergoing
apoptotic cell death, it represents a cellular “point of no
return”. Thus, a shift toward
lower BCL2/MCL1 with higher BAX/BAK reflects a pro-apoptotic BCL-2
family balance, favoring BAX/BAK activation, MOMP, and commitment to caspase-dependent apoptosis.
Our results suggest that at low-concentration agents, cells upregulate
pro-survival proteins in response to apoptotic signals, but at high
concentrations, this defense is overwhelmed, enabling MOMP and subsequent
apoptosis (Figure
B). Interestingly, BH3 (BCL2-homology-3)-only
proteins show selective NOXA primarily targets MCL-1, while BAD favors BCL-2 and BCL-XL. Structural
studies have shown that distinct amino acid substitutions underlie
the binding specificity of MCL1 and BCL-XL. This may explain our finding that,
under the highest CHX-CPC exposure, MCL1 was strongly
upregulated, while BCL2 declined, with BAX remaining suppressed, likely due to MCL1’s buffering effect.
These data highlight distinct regulatory roles for MCL1 and BCL2 despite their shared antiapoptotic function.
Cell-type-specific differences were also evident. hBMSCs showed greater resistance to cleaning agents than
MC3T3-E1 and HGFs, maintaining or even increasing BCL2 and MCL1 expression under concentrated NaClO, and
strongly upregulating MCL1 under CHX-CPC. One possible
explanation is hBMSĆs lower proliferation rate, which is associated
with reduced apoptotic priming, while rapidly dividing cells are generally
more prone to apoptosis, such as MC3T3-E1 and HGFs.
Several limitations of this study should be acknowledged.
First,
peri-implant tissues are composed of diverse cell populations beyond
those examined here. Future studies should therefore include peri-implant
epithelial cells, which form semidesmosome attachments and an internal
basal lamina, essential for epithelial sealing in the transmucosal
area, as well as immune cells such as polymorphonuclear leukocytes
and macrophages, which play key roles in bacterial eradication and
angiogenesis. Second, our in vitro model
cannot replicate the vascularized and inflammatory environment of
peri-implant tissues, where local and systemic immune responses shape
cytocompatibility. Moreover, clinical
peri-implantitis is characterized by complex biofilms dominated by
anaerobic pathogens (Porphyromonas gingivalis, Tannerella forsythia, Treponema denticola, and Fusobacterium
nucleatum), whose coexistence in an anaerobic, inflammatory
niche may profoundly alter peri-implant cell responses to chemical
residuals, for instance, oral bacteria in vivo rapidly degrade H2O2, likely diminishing its biological impact compared
with in vitro conditions. Third, technical
factors must be fetal bovine serum in the culture medium
can attenuate the cytotoxicity of H2O2, NaClO,
and CHX.
−
In this study, MC3T3-E1 cells and HGFs were cultured with FBS, whereas hBMSCs were maintained with platelet lysate, whose protective effects remain uncertain, thus, cross-cell comparisons, particularly regarding relative apoptosis resistance-should be made cautiously. Highest concentration dilution (1:5) in medium reduced the FBS from 10% to ∼8%, which may weaken protective support and potentially exaggerate cytotoxicity. Besides, primary human cells can exhibit donor-to-donor variability, confirmation of these findings using primary cells from multiple donors will be important before broader generalization. , These limitations underscore the need for more physiologically relevant models to evaluate the biological effects of residual chemical cleaning agents under clinically realistic conditions.
In summary, this study demonstrates that chemical debridement agents exert cytotoxic effects, impairing the proliferative viability of cells in peri-implant tissues in a time- and dose-dependent manner. In light of these findings, future therapeutic strategies for peri-implant mucositis and peri-implantitis should not rely solely on thorough chemical debridement but also incorporate biomaterials that activate tissue healing and regeneration.
This study demonstrated that residual chemical debridement agents in peri-implant pockets exert time- and dose-dependent cytotoxic effects on peri-implant cells under the conditions tested. However, all cell populations were negatively affected by agents that were not sufficiently removed. Within the limitations of this in vitro model, these findings underscore the importance of thoroughly removing residual decontamination agents to maintain peri-implant cell viability, implant biocompatibility, and a healing environment, as well as the need for additional biomaterials to stimulate healing and regeneration. From a translational perspective, our results support the rationale for rigorous rinsing after implant surface decontamination to facilitate peri-implant healing following peri-implantitis treatments. At the same time, further validation in more complex in vivo models is required.